Draft RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Prepared for The Boeing Company June 2015   Alexa Stamets, P.E., 65243  Program Manager      Contents Section  Page  Acronyms and Abbreviations ...................................................................................................................... v  1.0  Introduction ............................................................................................................................... 1‐1  1.1  Regulatory Framework .......................................................................................................... 1‐1  1.2  Scope, Purpose and Objective ............................................................................................... 1‐3  1.3  Document Organization ......................................................................................................... 1‐4  2.0  Summary of Site History and Existing Conditions ........................................................................ 2‐1  2.1  Site History ............................................................................................................................. 2‐1  2.2  Existing Conditions ................................................................................................................. 2‐1  3.0  Comprehensive DQO Evaluation for the EEL RFI Site ................................................................... 3‐1  3.1  Evaluation of Potential Contamination Sources .................................................................... 3‐1  3.2  Site‐specific Modeling or Evaluations Performed .................................................................. 3‐2  3.2.1  Air Dispersion Modeling ........................................................................................... 3‐2  3.2.2  Vapor Intrusion Pathway Evaluation ........................................................................ 3‐2  3.2.3  Vadose Zone to Groundwater Evaluation ................................................................. 3‐2  3.2.4  Groundwater Flow and Contaminant Transport Modeling ...................................... 3‐3  3.2.5  Human Health and Ecological Risk Assessment ........................................................ 3‐5  4.0  Data Summary by Media ............................................................................................................ 4‐1  4.1  Soil, Soil Vapor, and Vadose Zone Bedrock ........................................................................... 4‐1  4.1.1  Sanitary Sewer System Evaluation ............................................................................ 4‐2  4.1.2  Reclaimed Water System Evaluation ........................................................................ 4‐2  4.2  Groundwater and Seeps ........................................................................................................ 4‐3  5.0  Risk Assessment Summary .......................................................................................................... 5‐1  5.1  Human Health Risk Assessment Findings .............................................................................. 5‐1  5.1.1  COPC/ROPC Selection ............................................................................................... 5‐1  5.1.2  Exposure Assessment ............................................................................................... 5‐1  5.1.3  Estimated Risks and Hazards .................................................................................... 5‐2  5.1.4  Summary of Findings ................................................................................................ 5‐3  5.2  Ecological Risk Assessment Findings ...................................................................................... 5‐3  5.2.1  CPEC/RPEC Selection ................................................................................................ 5‐3  5.2.2  Exposure Assessment ............................................................................................... 5‐3  5.2.3  Estimated Risks and Hazards .................................................................................... 5‐4  5.2.4  Summary of Findings ................................................................................................ 5‐5  5.3  Uncertainties .......................................................................................................................... 5‐5  6.0  CMS and NFA Recommendations ................................................................................................ 6‐1  6.1  CMS Recommendations ......................................................................................................... 6‐1  6.1.1  Soil ............................................................................................................................. 6‐1  6.1.2  Soil Vapor .................................................................................................................. 6‐2  6.1.3  Vadose Zone ............................................................................................................. 6‐2  6.1.4  Groundwater and Seeps ........................................................................................... 6‐3  6.2  NFA Recommendations ......................................................................................................... 6‐3  7.0  References .................................................................................................................................. 7‐1  EN0317151003RDD III CONTENTS, CONTINUED   Section  8.0  Glossary of Terms ....................................................................................................................... 8‐1    Tables  3‐1  Assessment Elements for Identification of Potential Contamination Sources and Weight‐of‐ Evidence Documentation for CMS and NFA Recommendations for EEL RFI Site   Chemical Use Summary for EEL RFI Site   DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  Data Summary for Detected Results for EEL RFI Site (provided on CD only)    Data Summary for Nondetected Results for EEL RFI Site (provided on CD only)    DQO Evaluation Findings for EEL RFI Site – Groundwater and Seeps   Human Health Risk Estimates   Ecological Risk Estimates   CMS Area Recommendations   3‐2  4‐1  4‐2  4‐3  4‐4  5‐1  5‐2  6‐1    Figures   1‐1  2‐1  3‐1  4‐1  4‐2  4‐3  4‐4  4‐5  4‐6  4‐7  6‐1  Page  Boeing RFI Subareas  2007 Aerial Photo of EEL RFI Site   EEL RFI Site CUAs and CUA Clusters   Comparison of VOC Analytical Results to Characterization Levels for Soil and Soil Vapor from 0 to  10 feet Below Ground Surface, EEL RFI Site   Comparison of VOC Analytical Results to Characterization Levels for Soil and Soil Vapor Greater  than 10 feet Below Ground Surface, EEL RFI Site    Comparison of Other Analytical Results to Characterization Levels for Soil from 0 to 2 feet Below  Ground Surface, EEL RFI Site    Comparison of Other Analytical Results to Characterization Levels for Soil from 2 to 10 feet Below  Ground Surface, EEL RFI Site   Comparison of Other Analytical Results to Characterization Levels for Soil Greater than 10 feet  Below Ground Surface, EEL RFI Site   Estimated Footprint of Impacted Vadose Zone Bedrock for EEL RFI Site  Estimated Footprint of Impacted Groundwater for EEL RFI Site  Summary of CMS and NFA Area Recommendations, EEL RFI Site     Appendices  A  B  C  D  E    IV Sample Locations and Analytical Data for EEL RFI Site (provided as a pdf on the CD that accompanies  this report)  Air Dispersion Modeling and Sampling Summary (No Boeing sources were identified as requiring air  dispersion modeling at the EEL RFI site so Appendix B is not provided in this report)  Potential Transport of Contaminants in the Vadose Zone to Groundwater for EEL RFI Site  Groundwater Source Zone and Plume Characterization for EEL RFI Site  Human Health and Ecological Risk Assessment Findings for EEL RFI Site   EN0317151003RDD Acronyms and Abbreviations 3‐D  three‐dimensional  AOC  Administrative Orders on Consent  bgs  below ground surface  Boeing  The Boeing Company  BTV  background threshold value  CMS  corrective measures study  COC  chemical of concern  COEC  chemical of ecological concern  COPC  chemical of potential concern  CPEC  chemical of potential ecological concern  CUA  chemical use area  DCE  dichloroethene  DOE  United States Department of Energy  DQO  data quality objective  DSFR  Data Summary and Findings Report  DTSC  California Environmental Protection Agency, Department of Toxic Substances Control  EcoRBSL  ecological risk‐based screening level  EEL  Environmental Effects Laboratory  ELCR  estimated lifetime cancer risk  EMLC  estimated maximum leachate concentration  ERA  ecological risk assessment  GCL  groundwater comparison level  GCV  groundwater comparison value  HHRA  human health risk assessment    HI  hazard index  HQ  hazard quotient  MCL  maximum contaminant level  MCPA    2‐methyl‐4‐chlorophenoxyacetic acid  MWH  MWH International, Inc.  NASA  National Aeronautics and Space Administration  NFA  no further action  OU  Operable Unit  PAH  polycyclic aromatic hydrocarbon  EN0317151003RDD V ACRONYMS AND ABBREVIATIONS PCB  polychlorinated biphenyl  RBSL  risk‐based screening level  RCRA  Resource Conservation and Recovery Act  RFI  RCRA facility investigation  ROC  radionuclide of concern  ROPC  radionuclide of potential concern  RPEC  radionuclide of potential ecological concern  SCL  soil characterization level  SMCL  secondary maximum contaminant level  SQL  sample quantitation limit  SRAM  Standardized Risk Assessment Methodology  SSFL  Santa Susana Field Laboratory  STL‐IV  Systems Test Laboratory IV  STP‐3  Administrative Area III Sewage Treatment Plant  SVOC  semivolatile organic compound  SWRCB  California State Water Resources Control Board  TCE  trichloroethene  TEQ  toxicity equivalent  TPH  total petroleum hydrocarbons  USEPA  United States Environmental Protection Agency  VI  vapor intrusion  VI TM  Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory,  Ventura County, California  VOC  volatile organic compound    VI EN0317151003RDD SECTION 1  Introduction This report was prepared for The Boeing Company (Boeing) and presents the findings of the Resource  Conservation and Recovery Act (RCRA) Facility Investigation (RFI) for the Environmental Effects Laboratory  (EEL) RFI site located in Boeing RFI Subarea 5/9 South at the Santa Susana Field Laboratory (SSFL) in Ventura  County, California. The EEL RFI site is also known as the Hydrogen Laboratory. This report will herein be  referred to as the EEL RFI Data Summary and Findings Report (EEL DSFR). Subarea‐scale evaluations and a  summary of findings from all RFI sites in this subarea are presented in the associated Boeing RFI Subarea 5/9  South Data Summary and Findings Report, Santa Susana Field Laboratory, Ventura County, California (5/9S  DSFR) (CH2M HILL, 2015a).   1.1 Regulatory Framework The RCRA Corrective Action program at the SSFL began with the RCRA Facility Assessment in 1989. The RCRA  Facility Assessment was completed in 1994 and was followed by the RFI, which commenced in 1996 under the  oversight of the California Environmental Protection Agency, Department of Toxic Substances Control (DTSC).  Early characterization activities conducted at the SSFL are summarized in the RCRA Facility Investigation Program  Report, Surficial Media Operable Unit, Santa Susana Field Laboratory, Ventura County, California (MWH Global,  Inc. [MWH], 2004).   In 2007, the DTSC issued a Consent Order for Corrective Action (2007 Consent Order) (DTSC, 2007) that  identified the RCRA Corrective Action requirements for the SSFL to be implemented by Boeing, the United  States Department of Energy (DOE), and the National Aeronautics and Space Administration (NASA). For  corrective action, the 2007 Consent Order identifies two Operable Units (OUs) for investigation purposes.  The OUs at SSFL are:   The Surficial Media OU is composed of saturated and unsaturated soil, sediment, surface water, near‐ surface groundwater, air, biota, and weathered bedrock1. Near‐surface groundwater is groundwater  that occurs within the alluvium or weathered bedrock.    The Chatsworth Formation OU is composed of the Chatsworth Formation aquifer and both saturated  and unsaturated unweathered (competent) bedrock.  The 2007 Consent Order also identifies 11 Group Reporting Areas for the SSFL, referred to as RFI Groups  (Groups 1a, 1b, and 2 through 10). The Group Reporting Areas were established to provide a  comprehensive, integrated description of RFI site data from all media across large, interrelated areas of the  SSFL.   In 2010, DOE and NASA signed Administrative Orders on Consent for Remedial Action (AOCs) with DTSC that  govern characterization and remedial action activities for soil2 in portions of the SSFL in which their  operations occurred (DTSC, 2010a, 2010b). The DOE AOC includes Administrative Area IV and the Northern  Buffer Zone, and the NASA AOC includes Administrative Area II and a 40‐acre parcel of Administrative Area I,  where the Liquid Oxygen Plant was formerly located. The characterization and cleanup of soil in the areas  subject to the DOE and NASA AOCs are regulated by the AOCs. Media not subject to the AOCs (surface  water, groundwater, air, and biota) are regulated by the 2007 Consent Order.                                                                 1 Weathered bedrock at SSFL is considered the lithological profile of rock that meets the definition of W7 through W1, as described in Table 4‐4 of  the United States Bureau of Reclamation Engineering Geology Field Manual (United States Bureau of Reclamation, 1998), and above the first‐ encountered saturated zone.  2 This includes soil, sediment, weathered bedrock, debris, structures, and other anthropogenic materials, per the AOCs  EN0317151003RDD 1-1 SECTION 1 INTRODUCTION Boeing is completing the RCRA Corrective Action Program in accordance with the 2007 Consent Order.  However, due to the 2010 DOE and NASA AOCs, and with DTSC concurrence, Boeing restructured the RFI  Group Reporting Areas to account for AOC requirements. The portions of land that are not subject to the  DOE or NASA AOCs (that is, Administrative Areas I and III and the Southern Undeveloped Area) were  reorganized in 2013 into nine Boeing subareas for RFI reporting to complete the RFI in accordance with the  2007 Consent Order. The Boeing subareas are generally smaller footprints than the RFI Group Reporting  Areas to allow DTSC to more efficiently review the comprehensive RFI reports. The subareas comprise zero  to four RFI sites, and the surrounding undeveloped land (unaffiliated areas). As shown on Figure 1‐1, the  nine Boeing RFI subareas include:   5/9 South – includes portions of former Group 5 and Group 9 Reporting Areas   5/9 North – includes portions of former Group 5 and Group 9 Reporting Areas, as well as small portions  of former Group 3 and Group 6 Reporting Areas in the northern section of the subarea   10 – similar to Group 10 Reporting Area within the 2007 Consent Order   1A North – includes portion of former Group 1A Reporting Area   1A Central – includes portion of former Group 1A Reporting Area   1A South – includes portion of former Group 1A Reporting Area   1B North – includes portion of former Group 1B Reporting Area and portions of Groups 2 and 3    1B Southeast – includes portion of former Group 1B Reporting Area   1B Southwest – includes portion of former Group 1B Reporting Area  In addition to these nine subareas, Boeing will also prepare information for a SSFL‐wide groundwater report  as required by Sections 3.4.12 and 3.4.13 of the 2007 Consent Order.  A DSFR will be prepared for DTSC’s review for each of these Boeing RFI subareas and for each of the RFI sites  and areas unaffiliated with RFI sites within these Boeing RFI subareas. These DSFRs satisfy the administrative  requirements set forth in DTSC’s 2007 Consent Order, specifically including or addressing:   Section 3.4.2, which states that respondents shall submit to DTSC for approval RFI reports for the  Surficial Media OU, including a Large Home‐Range Ecological Risk Assessment Report.    Section 3.4.3, which states that the comprehensive Surficial Media OU reports shall summarize the  findings from all phases and areas of the SSFL, including all current and historical assessment data  collected to date, for the vicinity of the unit being investigated in the RFI program.    Sections 4.3 and 4.4, which state that the reports will be provided to DTSC for comment and approval,  and that Boeing will address DTSC comments prior to finalization of the reports.   In addition to the DSFRs, Boeing is submitting a separate deliverable to DTSC that includes historical  documents identified to contain information regarding site features, historical operations, and chemical and  radiological uses for the Boeing RFI subareas. Boeing previously provided DTSC with this information to  support DTSC’s review of RFI reports and work plans. This final, comprehensive historical document  deliverable satisfies the following 2007 Consent Order requirements:     1-2 Sections 3.4.4 and 3.4.5, which state that each respondent shall submit historical records and  documentation within its possession and control.  EN0317151003RDD SECTION 1 INTRODUCTION  Section 3.4.7, which states that respondents shall demonstrate and certify that they have conducted a  reasonable search for the documents required in Sections 3.4.4 and 3.4.5 and provide a signed copy of  the Signature and Certification page stipulated in Section 4.4.3 of the Consent Order to certify that a  reasonable search was completed for each Surficial Media OU report.  1.2 Scope, Purpose, and Objective This EEL DSFR pertains to the portions of the EEL RFI site located within Boeing RFI Subarea 5/9 South in  Administrative Area III. The portions of the EEL RFI site that are located within Administrative Area IV are  being characterized by DOE in accordance with the DOE AOC (DTSC, 2010a). This EEL DSFR summarizes and  evaluates data collected within the EEL RFI site reporting area boundary. As presented in Figure 1‐1, Boeing  RFI Subarea 5/9 South includes:   The eastern portion of Group 5 in Administrative Area III. This portion of the subarea includes the  following RFI sites:  - Systems Test Laboratory IV (STL‐IV) RFI site  Administrative Area III Sewage Treatment Plant (STP‐3) RFI site   Compound A Facility RFI site   EEL RFI site (Administrative Area III portion only)   The southern portion of Group 9 located between Administrative Areas II and IV and south of  Administrative Areas II, III, and IV. No RFI sites are located in this portion of Group 9. Most of this portion  of Group 9 is part of the Unaffiliated Areas of Boeing RFI Subarea 5/9 South.  Recent data‐gap analysis and investigations have been performed at the EEL RFI site in accordance with the  Master Resource Conservation and Recovery Act Facility Investigation Data Gap Work Plan, Santa Susana  Field Laboratory, Ventura County, California (Master RFI Data Gap Work Plan) (CH2M HILL, 2013a) and the  Comprehensive Data Quality Objectives Report, RCRA Facility Investigation, Santa Susana Field Laboratory,  Ventura County, California (DQO Report) (CH2M HILL, 2013b). The Master RFI Data Gap Work Plan presents the  overall framework for applying the SSFL comprehensive data quality objectives (DQOs) to the Boeing RFI  subareas and for completing the RFI. The DQO Report presents the process for completing characterization of the  nature and extent of any known release, for evaluating the transport and fate of contaminants, and for assessing  risk to human and ecological receptors to support RCRA corrective measures study (CMS) and no further action  (NFA) recommendations.   This EEL DSFR builds upon the information and data presented in Group 5 – Central Portions of Areas III and  IV RCRA Facility Investigation Report, Santa Susana Field Laboratory, Ventura County, California (Draft Group  5 RFI Report) (CH2M HILL, 2008), Appendix G of which presented the RFI report for the EEL RFI site (Draft  EEL RFI Site Report). While that report presented preliminary risk assessment findings and CMS  recommendations for the EEL RFI site, additional evaluation of potential sources of contamination has been  performed, and additional data have been collected in accordance with the DQO Report.   In addition, DTSC provided comments on the Draft Group 5 RFI Report (DTSC, 2009, 2010c, 2010d, 2012),  and Boeing provided responses to those DTSC comments in the Master RFI Data Gap Work Plan, Addendum  to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa  Susana Field Laboratory, Ventura County, California (EEL Work Plan Addendum) (CH2M HILL, 2013c), and  Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI Subarea 5/9 South, STL‐IV  RFI Site, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2013d). DTSC’s prior  comments on the 2008 Draft EEL RFI Site Report (CH2M HILL, 2008) were also considered during preparation  of this EEL DSFR.   This EEL DSFR is being submitted to DTSC as a draft document. Following receipt of written DTSC comments  on this draft EEL DSFR, Boeing will revise the document to address DTSC’s comments and submit a revised  EN0317151003RDD 1-3 SECTION 1 INTRODUCTION EEL DSFR to DTSC in accordance with Section 4.3 of the 2007 Consent Order. Upon DTSC’s approval of the  EEL DSFR, the EEL DSFR will serve as the Final RFI report for the EEL RFI site.   Together, this EEL DSFR, along with all other Boeing subarea and RFI site DSFRs, and the forthcoming Large‐ Home‐Range Ecological Risk Assessment Report, once approved by DTSC, will meet the requirements  presented in Section 3.4.2 of the 2007 Consent Order.  The purpose of this EEL DSFR is to:   Summarize the identified sources of contamination, characterization data, and applicable migration  pathways for the EEL RFI site.    Summarize the findings of the human health and ecological risk assessments, vadose zone mass‐flux‐to‐ groundwater evaluation, and groundwater source zone evaluation performed for the EEL RFI site.   Present recommendations for corrective measure areas for the EEL RFI site based on the RFI  characterization and risk assessment findings in accordance with Sections 3.4.2 and 3.4.3 of the 2007  Consent Order.   1.3 Document Organization This EEL DSFR is organized as follows:  Section 1 – Introduction. This section provides an introduction to the report, including the purpose and  objective.  Section 2 – Summary of Site Conditions. This section provides a summary of the site conditions, including  historical uses, surface water features, and geologic and hydrogeologic setting.  Section 3 – Comprehensive DQO Evaluation for the EEL RFI Site. This section presents the chemical use  areas (CUAs) that were identified at the EEL RFI site through implementation of the DQO process and  describes the transport‐ and risk‐related modeling and assessments performed.  Section 4 – Data Summary by Media. This section presents a summary of the data collected, including  conclusions regarding the nature and extent and transport and fate of chemicals in environmental media.  Section 5 – Risk Assessment Summary. This section presents a summary of the human health and ecological  risk assessment findings.  Section 6 – CMS and NFA Recommendations. This section presents a summary of the CMS and NFA  recommendations.  Section 7 – References. This section presents a list of references used to prepare this report.  Appendices. Site‐specific evaluations and risk assessments performed for the EEL RFI site are presented in  the following appendices:   Appendix A: Sample Locations and Analytical Data for EEL RFI Site   Appendix B: Air Dispersion Modeling and Sampling Summary (which is not applicable to the EEL RFI site;  therefore, not included in this EEL DSFR)   Appendix C: Potential Transport of Contaminants in the Vadose Zone to Groundwater for the EEL RFI  Site   Appendix D: Groundwater Source Zone and Plume Characterization for the EEL RFI Site   Appendix E: Human Health and Ecological Risk Assessment Findings for the EEL RFI Site   Other site‐specific DSFRs pertaining to the other RFI sites within Boeing RFI Subarea 5/9 South (namely, the  STL‐IV, STP‐3, and Compound A Facility RFI sites) and pertaining to the areas unaffiliated with RFI sites in  1-4 EN0317151003RDD SECTION 1 INTRODUCTION Boeing RFI Subarea 5/9 South provide similar information for the remaining portions of Boeing RFI Subarea  5/9 South. The results of subarea‐scale evaluations and a summary of findings for the RFI sites and  unaffiliated areas in Boeing RFI Subarea 5/9 South are presented in the 5/9S DSFR (CH2M HILL, 2015a).  EN0317151003RDD 1-5 SECTION 2  Summary of Site History and Existing Conditions The EEL RFI site is located on the boundary between Administrative Areas III and IV in the western portion of  the SSFL. As noted above, this EEL DSFR pertains to the portions of the EEL RFI site located within Boeing RFI  Subarea 5/9 South in Administrative Area III. The portions of the EEL RFI site that are located within  Administrative Area IV are being characterized by DOE in accordance with the DOE AOC (DTSC, 2010a). The  site is currently inactive, and all structures have been demolished. A summary of the site history and existing  conditions is provided below. Additional detailed information on the historical use and site conditions at the  EEL RFI site are presented in the Draft EEL RFI Site Report (CH2M HILL, 2008) and the EEL Work Plan  Addendum (CH2M HILL, 2013c).   2.1 Site History 2.2 Existing Conditions Buildings 3268 and 3271 were identified as Solid Waste Management Unit 6.9 in the RCRA facility  assessment (Science Applications International Corporation [SAIC], 1994) and were used for the EEL  Cryogenic Laboratory and associated test cells from 1968 through 2008. These buildings were used for  testing various materials under high‐pressure hydrogen conditions. Other structures associated with the  testing operations included an equipment and material storage building, a mechanics workshop, a  hazardous materials storage pad, transformers, and over 25 small aboveground storage tanks that were  mostly used to store gases and hydraulic oil. Some of the historical site features are shown on Figure 2‐1,  which presents an aerial photograph of the EEL RFI site from 2007.  Topography in the eastern‐central portion of the EEL RFI site reporting area slopes to the south and east.  Topography in the western portion of the EEL RFI site reporting area slopes to the south and west. The EEL  RFI site is located north of the Burro Flats Fault near the Silvernale Member of the Upper Chatsworth  Formation. Beds of the Silvernale Member generally strike N70°E and dip 25°NW. The Silvernale Member is  predominantly composed of medium‐grained sandstone with minor siltstone‐sandstone units. Additional  geologic information is presented in Appendix B of the Group 5 RFI Report (CH2M HILL, 2008).  Throughout most of the EEL RFI site, soil is generally thin, typically ranging from less than 3 feet to 10 feet  thick. There are no bedrock outcrops at the EEL RFI site. Fill soil is primarily composed of fine‐grained silty  sands, clayey sandy silts, silty clays, and lean clay. Soil in the undisturbed areas of the EEL RFI site consists of  weathered Chatsworth Formation materials, which are primarily fine‐grained, silty sands, and clayey silts.  Groundwater at the EEL RFI site is approximately 18 to 20 feet below ground surface (bgs).   Surface water exists intermittently in ephemeral drainage channels at the western end of the EEL RFI site as  the result of seasonal precipitation events. Surface water in the ephemeral drainage channels flows south  through the Compound A Facility RFI site, and ultimately to the R‐2 Ponds in Administrative Area II. Surface  water runoff in the other parts of the EEL RFI site flows via sheet flow generally south to the pond at the  STP‐3 RFI site.  EN0317151003RDD 2-1 SECTION 3  Comprehensive DQO Evaluation for the EEL RFI Site The approach and process for the comprehensive DQO evaluation is summarized in the 5/9S DSFR (CH2M  HILL, 2015a). This section presents the CUAs that were identified at the EEL RFI site through implementation  of the DQO process and describes the transport‐ and risk‐related modeling and assessments performed for  the EEL RFI site. Appendix A presents a figure and tables representing the samples for media representative  of current conditions at the EEL RFI site and evaluated in this DSFR. The analytical data were compiled from  various sources including, but not limited to, data‐gap sampling, groundwater monitoring, and confirmation  sampling. Section 4 of this EEL DSFR presents a summary of the analytical data used to characterize  environmental media and to evaluate the applicable migration pathways at the EEL RFI site.   3.1 Evaluation of Potential Contamination Sources The detailed approach for identifying potential sources of contamination is presented in the DQO Report  (CH2M HILL, 2013b) and the Master RFI Data Gap Work Plan (CH2M HILL, 2013a). As presented in the DQO  Report, the following five methods were used to verify that all potential sources of contamination were  identified and investigated within the Boeing RFI subareas: (1) document and record review; (2) SSFL  sitewide inventories (building features, tanks, sewer system, reclaimed water system, and pipelines); (3)  SSFL sitewide comprehensive inspections and documentation; (4) RFI site‐specific inspections and  documentation; and (5) chemical migration assessment. Table 3‐1 presents a comprehensive summary of  the weight‐of‐evidence assessment of any known or potential release of any chemical previously used,  stored, handled, or disposed within the EEL RFI site; this table serves to document the completeness of the  DQO process for identifying potential contamination sources. Areas of suspect or potential chemical use,  storage, handling, or disposal were identified as potential CUAs and screened for potential releases using  the field sampling methodologies described in the DQO Report. If the concentrations detected in the  screening level sample(s) were above characterization levels,3 the potential CUA was identified as a new  CUA or added to an existing CUA unless it is determined that the analytes detected in the sample are  associated with a different feature or potential release and are unlikely to be associated with the potential  CUA.  Sixteen CUAs have been identified at the EEL RFI site, as presented in Table 3‐2 and on Figure 3‐1. For the  purposes of evaluation, CUAs were renumbered from what was presented in the Draft EEL RFI Site Report  (CH2M HILL, 2008) such that each individual CUA was assigned an individual number for identification. In  addition, CUAs have been combined into CUA clusters based on similarities in operational history,  geographic proximity, lithologic features, analytical data, and previous CMS recommendations. Every  location where a chemical has been detected above a corresponding characterization level has also been  included in a CUA cluster. One CUA cluster (CUA Cluster 1) has been identified at the EEL RFI site.   Following the process presented in the DQO Report, potential CUAs A and B (the western and eastern STL‐IV  reclaimed water spray fields, respectively) were identified at the EEL RFI site, as documented in the EEL  Work Plan Addendum (CH2M HILL, 2013c). After completion of screening‐level sampling to characterize the  potential CUAs, some results exceeded soil characterization levels (SCLs), and potential CUAs A and B were  reassigned as CUAs 15 and 16, respectively. A portion of potential CUA A that included a structure north of  Building 3905 is excluded from CUA 15 because screening‐level data were below characterization levels at                                                               3 Characterization levels are based on the higher of the 1) Combined Strata 95‐95 Upper Tolerance Limit background threshold values (for chemicals  that have such values) and 2) lowest of either the Suburban Residential Risk‐based Screening Levels (RBSLs) or Ecological Low RBSLs. Characterization  levels for some chemicals are established as the method reporting limit that can be achieved by multiple laboratories if achieving the risk‐ or  background level‐based characterization level is deemed technically limited and/or infeasible.  EN0317151003RDD 3-1 SECTION 3 COMPREHENSIVE DQO EVALUATION FOR THE EEL RFI SITE this structure. In addition, a portion of potential CUA B that included a section of reclaimed water pipeline is  excluded from CUA 16 because screening‐level data were below characterization levels at this pipeline  section.   A summary of the sources, operational history, and site conditions for each CUA and potential CUA is  presented in Section 4. Section 4 also summarizes the results of the characterization performed at potential  CUAs that support the conclusions described above.  3.2 Site-specific Modeling or Evaluations Performed The following text describes the site‐specific transport‐ and risk‐related modeling and assessments that  were performed for the EEL RFI site to support the conclusions presented in Section 4 of this DSFR. Other  modeling and assessments are performed at the subarea scale and are consequently described in the 5/9S  DSFR (CH2M HILL, 2015a).   3.2.1 Air Dispersion Modeling Air dispersion modeling was performed for the representative sources in the Boeing RFI subareas identified  in Appendix B of the DQO Report, Recommended Approach for Air Dispersion Modeling, Boeing RCRA Facility  Investigation Project (CH2M HILL, 2013e). The approach for assessing air deposition impacts for other  potential Boeing sources at SSFL, based on the results of the modeling of representative sources, is  presented in Air Dispersion Evaluation Approach for Other Boeing Sources at Santa Susana Field Laboratory,  Ventura County, California (CH2M HILL, 2014b). No sources at the EEL RFI site were identified as requiring air  dispersion modeling during this process; therefore, air dispersion modeling was not performed for the EEL  RFI site.    3.2.2 Vapor Intrusion Pathway Evaluation The Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura  County, California (VI TM) (CH2M HILL, 2015d) presents an evaluation of the vapor intrusion (VI) migration  pathway and recommendations for filling data gaps to support future evaluation of the VI pathway for each  RFI site in Boeing RFI Subarea 5/9 South. As discussed in the 5/9S DSFR, the occurrence of volatile organic  compounds (VOCs) in soil vapor at concentrations above VI characterization levels (which are based on  default regulatory attenuation factors) at Boeing RFI Subarea 5/9 South appears to be more strongly  associated with residual VOCs in the vadose zone associated with releases from CUAs rather than off‐gassing  from groundwater.   At the EEL RFI site, a VOC groundwater plume is estimated to underlie much of the site, based on  groundwater data and estimated flow paths from the groundwater flow model. The results of the VI  pathway evaluation for the EEL RFI site are summarized in Section 4 of this EEL DSFR. The VI pathway is  further evaluated as part of the human health risk assessment (HHRA), the results of which are presented in  Appendix E and summarized in Section 5 of this EEL DSFR.   3.2.3 Vadose Zone to Groundwater Evaluation The vadose zone to groundwater evaluation involved a comprehensive review of vadose zone and  groundwater data, and vadose zone to groundwater transport modeling at the EEL RFI site for CUA Cluster 1.    Available soil matrix and soil vapor vadose zone data were evaluated for the EEL RFI site. These data were  first screened against either background threshold values (BTVs) or groundwater comparison values (GCVs,  which are numerically equivalent to groundwater characterization levels [GCLs] presented in Section 3.2.4)  as presented in Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to  Groundwater (MWH, 2013), with applicable updates to regulatory screening levels if the updated levels are  lower than those presented in Appendix D of the DQO Report. Additional screening levels were developed  and documented in the Final Development of Risk Based Screening Levels for Additional Groundwater  Constituents and Screening Level Clarifications (MWH, 2014a) and the Draft Development of Risk Based  Screening Levels for Additional Groundwater Constituents Detected at the Santa Susana Field Laboratory  3-2 EN0317151003RDD SECTION 3 COMPREHENSIVE DQO EVALUATION FOR THE EEL RFI SITE (MWH, 2014b). Consistent with the DQO framework and the Recommended Approach for Evaluating Vadose  Zone Mass Flux of Contaminants to Groundwater (MWH, 2013), BTVs were used for screening of vadose  zone data, if available, and GCVs were used if BTVs were not available.    For those chemicals exceeding BTVs/GCVs, transport from the vadose zone to groundwater was modeled  using the Seasonal Soil compartment model (SESOIL) Version 7.1, following the methods and procedures  outlined in Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater  (MWH, 2013). Chemicals were recommended for CMS in the vadose zone for groundwater protection or  NFA based on the results of the evaluation. Results are summarized in Section 4.1. Detailed information on  the evaluation methodology, field work performed, and results and recommendations are presented in  Appendix C.  3.2.4 Groundwater Flow and Contaminant Transport Modeling Site data and the three‐dimensional (3‐D) groundwater flow model developed for SSFL, as presented in the  Draft Site‐Wide Groundwater Remedial Investigation Report, Santa Susana Field Laboratory, Ventura County,  California (MWH, 2009) were used to help evaluate groundwater flow directions at the EEL RFI site. The flow  model was used to create forward and backward particle tracks (that is, flow paths). CUA cluster‐specific  forward particle tracks for pumping and non‐pumping conditions were developed for this evaluation to  estimate the extent of chemical transport from likely or confirmed sources at the CUA cluster at the EEL RFI  site. Forward particle path lengths were truncated based on the mean Darcy flux at the EEL RFI site as  estimated from the 3‐D flow model. The approach for estimating transport distances based on mean Darcy  flux at the EEL RFI site is discussed in Appendix D. Wells interpreted to intercept groundwater flow from the  EEL RFI site were identified based on review of these truncated particle tracks.    Impacts to seeps or offsite wells from the EEL RFI site are of little to no consequence in light of its distant  location from, and magnitude of releases relative to, the location of these features. For a discussion of seeps  in Boeing RFI Subarea 5/9 South, refer to the STL‐IV RFI site DSFR (CH2M HILL, 2015e).  Available groundwater sampling results for wells interpreted to monitor the EEL RFI site were evaluated for  the period of record through 2014. Preliminary data for wells ES‐29 and RS‐37 from the first quarter of 2015,  which were collected to satisfy data‐gap sampling recommendations for EEL, were also included. The  following 11 chemical groups with chemicals detected above their respective screening values in the vadose  zone at the EEL RFI site were evaluated for potential releases to groundwater within and downgradient of  the site:              VOCs  Semivolatile organic compounds (SVOCs) – phthalates   Polycyclic aromatic hydrocarbons (PAHs)  Energetics ‐ perchlorate  Total petroleum hydrocarbons (TPHs)  Polychlorinated biphenyls (PCBs)  Herbicides  Pesticides  Dioxins and furans  Metals  Inorganics  These data were screened against the GCLs used in the Potential Transport of Contaminants in Vadose Zone  to Groundwater (Appendix C of this report) to evaluate the presence of chemicals at concentrations above  their GCLs at the site and to identify data gaps. The GCLs used for the evaluation are groundwater reference  values, listed as follows, in approximate descending order of importance and/or relevance:  EN0317151003RDD 3-3 SECTION 3 COMPREHENSIVE DQO EVALUATION FOR THE EEL RFI SITE  Site‐specific groundwater comparison concentrations for metals and selected inorganic compounds  developed by DTSC (MWH, 2014c)   Isotope‐specific activity limits for individual beta/photon emitters based on the effective dose  equivalent of 4 millirems per year (Federal Register, 2000)   Primary maximum contaminant levels (MCLs) established by the United States Environmental Protection  Agency (USEPA) and promulgated by the Safe Drinking Water Act, and the California State Water  Resources Control Board (SWRCB) Division of Drinking Water, promulgated by Title 22 of the California  Code of Regulations, Sections 64431 through 64449 and 64672 (SWRCB, 2014a‐b)   Notification levels/advisory levels established by the California SWRCB (SWRCB, 2014b, 2015a‐b).   Secondary maximum contaminant levels (SMCLs), which are non‐mandatory, unenforced levels to  address aesthetics such as taste and odor (SWRCB, 2006, 2014b; USEPA, 2009)   Taste and odor thresholds (SWRCB, 2014b)   Site‐specific values developed for SSFL using risk assessment procedures assuming direct ingestion of  groundwater   For chemicals with more than one reference value, the lower value is used to be conservative. For example,  when USEPA and California SWRCB MCL values differ, the lower value is used, and in cases where the SMCL  is lower than the primary MCL, the SMCL is used. The methodology used to develop risk‐based screening  values for nonmetals and chemicals without agency‐published values is described in a technical  memorandum included in Appendix 7‐C of the Draft Site‐Wide Groundwater Remedial Investigation Report,  Santa Susana Field Laboratory, Ventura County, California (MWH, 2009). Additional risk‐based screening  levels were developed and documented in Final Development of Risk Based Screening Levels for Additional  Groundwater Constituents and Screening Level Clarifications (MWH, 2014a) and Draft Development of Risk  Based Screening Levels for Additional Groundwater Constituents Detected at the Santa Susana Field  Laboratory (MWH, 2014b). Groundwater reference values are presented in Table 9 of the 2014 Report on  Annual Groundwater Monitoring (MWH, 2015).  A source zone evaluation was performed to identify chemicals of concern (COCs) in groundwater sourced  from the EEL RFI site. Assessment of the nature and extent of chemical impacts to groundwater beneath the  EEL RFI site was performed by evaluating recent (2010 to 2014) and historical groundwater data. The fate  and transport of chemicals in groundwater at the EEL RFI site was evaluated using plume stability analysis  involving chemical trend analysis, vapor intrusion evaluation (CH2M HILL, 2015c), and evaluation of natural  attenuation processes.    Statistical trend analysis was performed to evaluate trends in concentration over time for chemicals  identified as sources in the vadose zone at the EEL RFI site and chemicals detected in groundwater above  GCLs in recent data (2010 to 2014) for wells in the vicinity of the EEL RFI site. Groundwater data for these  chemicals collected between 1984 and 2014 from wells selected for evaluation of the EEL RFI site were used  for the trend analysis. If trichloroethene (TCE) was included in the list of chemicals, TCE daughter products  (1,1‐dichloroethene [DCE], cis‐1,2‐DCE, trans‐1,2‐DCE, and vinyl chloride) were also evaluated in the trend  analysis. Trend analysis was performed for chemicals at well locations where greater than three sample  results were available and greater than 25 percent of total sample results had detections. The trend analysis  was performed using the Mann Kendall test at a 99 percent confidence level using the commercially  available, public‐domain ProUCL software package. Nondetect results considered in the trend analysis were  replaced with half of the quantitation limit. This method for trend analysis is consistent with the alternatives  identified in the DQO Report (CH2M HILL, 2013b). The methodology used for the trend analysis is  summarized in a flowchart provided as Figure D‐3 in Appendix D.  Detailed information on the groundwater flow and contaminant transport evaluation for the EEL RFI site is  summarized in Section 4.2 and further described in Appendix D.  3-4 EN0317151003RDD SECTION 3 COMPREHENSIVE DQO EVALUATION FOR THE EEL RFI SITE 3.2.5 Human Health and Ecological Risk Assessment Human health and ecological risk assessments were performed for the EEL RFI site in accordance with the  Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory,  Ventura County, California (SRAM Rev. 2 Addendum) (MWH, 2014c). For human health, risks were  calculated for exposure to soil by hypothetical suburban residents and recreational users, for indoor air  exposures to soil vapor by hypothetical suburban residents, and for exposure to groundwater by  hypothetical future residents through direct exposure. Human health risks associated with the hypothetical  future domestic use of groundwater are evaluated at the subarea scale, as presented in Appendix C of the  5/9S DSFR (CH2M HILL, 2015a).   Ecological risks were evaluated for the EEL RFI site for exposure to soil by birds and mammals through direct  contact, ingestion, or bioaccumulation in the food chain; for exposure to soil vapor by burrowing mammals  through intrusion into burrows; and for exposure to shallow groundwater (where depth to groundwater is  less than 6 feet bgs) by birds and mammals through direct contact or ingestion.   Risks for large‐home‐range ecological receptors across Boeing RFI Subarea 5/9 South will be calculated in  accordance with the SRAM Rev. 2 Addendum and will be presented in a separate document.   The results of these risk assessments for the EEL RFI site are presented in Appendix E and summarized in  Section 5.     EN0317151003RDD 3-5 SECTION 4  Data Summary by Media This section presents a summary of the data collected at the EEL RFI site, including conclusions regarding the  nature and extent and transport and fate of chemicals in environmental media. Additional data were  collected by DOE and provided to Boeing after preparation of the EEL DSFR had commenced. These data are  therefore evaluated separately in Attachment C‐5 of Appendix C and in Appendix E4.  4.1 Soil, Soil Vapor, and Vadose Zone Bedrock Table 4‐1 summarizes the nature and extent and fate and transport evaluations performed for soil, soil  vapor, and vadose zone bedrock at the EEL RFI site. Table 4‐1 provides a summary of the migration pathways  applicable to chemicals at the EEL RFI site (migration via air dispersion and deposition, migration of VOCs to  air, migration via surface water, and migration to vadose zone bedrock and mass flux to groundwater).  Table 4‐1 also includes a summary of the components of the sanitary sewer and reclaimed water sitewide  systems within the EEL RFI site, as well as the analytical data used to evaluate the potential for releases from  those sitewide systems within the EEL RFI site.   Tables 4‐2 and 4‐3, which are provided electronically on the CD that accompanies this report, present details  on the detect and nondetect sample results, respectively, exceeding characterization levels. Figures 4‐1  through 4‐5 present summaries of the soil and soil vapor characterization performed to date at the EEL RFI  site. Sampling results are presented on figures for VOCs and for all analytes other than VOCs for various  depth intervals. In addition, based on risk assessment and vadose zone to groundwater modeling, areas  recommended for CMS evaluation are shown on these figures and discussed in Section 6. Appendix A  presents a figure and tables of all samples for all media representative of current conditions at the EEL RFI  site.  The source areas at the EEL RFI site include the area around operational buildings, hazardous materials  storage pads, transformers, storage tanks, and the reclaimed water spray fields. The chemical groups most  frequently detected above SCLs are PCBs, dioxins and furans, and metals in soil. With the exception of  dioxins and furans, the exceedances of these chemical groups above SCLs are generally consistent with the  historical operations performed at the EEL RFI site. As presented in Table 4‐1, the extents of these  exceedances are defined by analytical results less than SCLs, nondetect results, or the presence of bedrock.  The exceedances of dioxins and furans above the SCL occur mostly in the surface soil and are found both  within operational and non‐operational areas of the EEL RFI site. Dioxins and furans have also been detected  above the SCL in shallow soil at nearby RFI sites, and their occurrence is not limited to past operational  areas. Furthermore, dioxins and furans detected above the SCL in samples collected within the drainage  channel at the western end of the EEL RFI site have likely migrated from upgradient locations. Although  dioxins and furans are not defined to below SCLs within the footprints of the EEL RFI site, dioxins and furans  are generally defined to below the SCL on a regional scale.  VOCs (specifically, benzene, toluene, and TCE) have been detected at concentrations exceeding soil vapor  characterization levels (SVCLs) at the EEL RFI site. Exceedances of benzene, toluene, and TCE in soil vapor are  also generally located in the historical operational areas of the EEL RFI site. As presented in Table 4‐1, the  extents of these exceedances are defined by analytical results less than SVCLs, nondetect results, or the  presence of bedrock.  Chemicals exceeding their respective BTVs or GCVs in vadose zone samples were further evaluated by  transport modeling for transport from the vadose zone to groundwater and for future protection of  groundwater according to methodology described in Appendix C. The following chemicals were detected in  vadose zone samples collected at the EEL RFI site at concentrations that exceed vadose zone concentrations  protective of groundwater based on transport modeling estimates:  EN0317151003RDD 4-1 SECTION 4 DATA SUMMARY BY MEDIA      One VOC (TCE)  One energetic (perchlorate)  Two herbicides (2,4‐dichlorophenoxybutyric acid, 2‐methyl‐4‐chlorophenoxyacetic acid)  Three pesticides (beta‐benzene hexachloride, heptachlor, helptachlor epoxide)  One inorganic (nitrate‐NO3)  The area of impacted bedrock was estimated by reviewing available rock core pore water data in  combination with surrounding soil vapor, soil, and groundwater data collected at the RFI site. To project the  area of impacted bedrock for areas where no rock core data were available, the other site data (soil, soil  vapor, and groundwater) were reviewed considering the chemical concentrations relative to their screening  values, the chemical properties, the depth of highest chemical concentrations relative to bedrock, and the  vadose zone to groundwater transport modeling predictions for the area. Figure 4‐6 shows the estimated  footprint of impacted bedrock at the EEL RFI site using the logic described above.     An evaluation was also conducted of the analytical data to identify potential releases above characterization  levels from the sitewide sanitary sewer system and reclaimed water system. Summaries of each of these  evaluations are presented below.  4.1.1 Sanitary Sewer System Evaluation An evaluation was conducted to identify potential releases of chemicals or radionuclides associated with the  sitewide sanitary sewer system in Boeing RFI Subarea 5/9 South. The Sanitary Sewer System Assessment for  Boeing RFI Subareas Technical Memorandum, Santa Susana Field Laboratory, Ventura County, California  (Sanitary Sewer TM) (CH2M HILL, 2015b) presents a compilation of information, including sanitary sewer  system segments, known and suspected inputs to the system, and potential chemicals and radionuclides  that may be associated with the system. As documented in the Sanitary Sewer TM, there are approximately  750 feet of sanitary sewer pipeline and two sanitary sewer manholes within the EEL RFI site.   Analytical data collected near the sanitary sewer system features within the EEL RFI site were evaluated for  the chemicals and radionuclides associated with the sanitary sewer system. A summary of the  characterization performed along the sanitary sewer system in the EEL RFI site is presented in Table 4‐1. As  presented in Table 4‐1, based on the review of the analytical data, potential releases from the sanitary  sewer system are not expected to have resulted in chemical or radiological constituents at concentrations  exceeding characterization levels in environmental media at the EEL RFI site.   4.1.2 Reclaimed Water System Evaluation An evaluation was conducted to identify potential releases of chemicals and radionuclides associated with  the reclaimed water portion of the water conveyance system in Boeing RFI Subarea 5/9 South. The  Reclaimed Water System Assessment for Boeing RFI Subareas, Santa Susana Field Laboratory, Ventura  County, California (Reclaimed Water System TM) (CH2M HILL, 2015c) presents a summary of the  components of the reclaimed water portion of the water conveyance system, potential inputs to the system,  and potential chemicals and radionuclides that may be associated with the system (CH2M HILL, 2015b). As  presented in the Reclaimed Water System TM, there are two spray fields and approximately 550 feet of  reclaimed water pipeline within the EEL RFI site.  Analytical data collected from sprayfield areas and along pipelines were evaluated for the chemicals and  radionuclides associated with reclaimed water systems. A summary of the characterization performed along  the reclaimed water system in the EEL RFI site is presented in Table 4‐1. As presented in Table 4‐1, 4,4’‐DDT  and SVOC concentrations in soil may be associated with potential releases from the sprayfields. The 4,4’‐ DDT and SVOC detections exceeding SCLs are defined, and the results for surface soil indicate that these  chemicals do not appear to be migrating via surface water migration, based on downgradient soil sampling  results, which are below SCLs.    4-2 EN0317151003RDD SECTION 4 DATA SUMMARY BY MEDIA 4.2 Groundwater and Seeps The chemical groups evaluated in the groundwater source zone and plume characterization evaluation for  the EEL RFI site in Appendix D includes those that were present in the vadose zone and/or groundwater  above screening levels: VOCs, SVOCs, PAHs, energetics, petroleum hydrocarbons, PCBs, herbicides,  pesticides, dioxins and furans, metals, and inorganics. Table 4‐4 provides groundwater source zone and  plume characterization information at the EEL RFI site by chemical group and provides a summary of  recommended actions.  Additional groundwater samples were collected from existing wells for completing the vadose zone to  groundwater (Appendix C) and groundwater source zone and plume characterization (Appendix D)  evaluations. One new well (RS‐37) was installed in December 2013 in the southeastern portion of EEL CUA  Cluster 1 to replace well RS‐17 (which had insufficient water for sampling) to monitor flow paths under the  current non‐pumping condition. Information on the groundwater sampling and well installation conducted  for completion of the vadose zone to groundwater evaluation is described in Section C.3 of Appendix C.  Additional groundwater sampling is described in Section D.3 of Appendix D.  VOCs represent the greatest groundwater impacts at the EEL RFI site because they are found at the greatest  extent and highest concentrations relative to their GCLs of chemicals sourced from the EEL RFI site. VOCs  detected in groundwater at concentrations above GCLs in recent data (2010 to 2014) sourced from the EEL  RFI site include cis‐1,2‐DCE and TCE. TPH and metals were also detected in groundwater at concentrations  above GCLs in recent data, but the impacts to groundwater are within the extent of the VOC impacts.   Concentrations of cis‐1,2‐DCE and TCE were above GCLs in samples collected at RS‐15 during 2011 sampling.  Additionally, concentrations of TCE were detected above GCLs in ES‐29 during 2010, 2012, and 2014  sampling and ES‐30 during 2010 sampling. The lateral extent of VOCs in groundwater at the EEL RFI site  extends beyond site boundaries due to impacts from adjacent RFI sites. The VOC impacts are currently  defined by RS‐17 and RS‐37 to the southwest, PZ‐028 to the northeast, PZ‐051 to the northwest, and wells in  the southwest drainage to the south (that is, SP‐882 and RD‐06). The lateral extent of impacted  groundwater at the EEL RFI site is presented on Figure 4‐7. Although there are no vertically discrete  sampling locations within the EEL RFI site, sampling results from the vertical clusters to the west and  southwest near STL‐IV (RD‐55 and RD‐58 clusters) and to the south of the Burro Flats Fault (SP‐882G) show  that VOCs have been characterized to below or near GCLs. Three‐dimensional plume evaluations have been  developed for groundwater impacts in Boeing RFI Subarea 5/9 South; descriptions and results are presented  in Appendix B of the 5/9S DSFR (CH2M HILL, 2015a).  Impacts to seeps or offsite wells from the EEL RFI site are of little to no consequence in light of its distant  location from, and magnitude of releases relative to, the location of these features. For a discussion of seeps  in Boeing RFI Subarea 5/9 South, refer to the STL‐IV RFI site DSFR (CH2M HILL, 2015e).  The potential transport of chemicals of concern at the EEL RFI site was assessed by plume stability analysis.  Statistical trend analysis was performed to evaluate trends in concentration over time for chemicals  identified as sources in the vadose zone at the EEL RFI site and chemicals detected in groundwater above  GCLs in recent data (2010 to 2014) for wells in the vicinity of the EEL RFI site. Trend analysis results are  summarized by well and chemical in Appendix D. No increasing chemical trends were identified in samples  collected from wells in the vicinity of the EEL RFI site. Chemical trends were either decreasing or  indeterminate at the 99 percent confidence level, indicating that impacts to groundwater at the EEL RFI site  are not expanding. The following decreasing trends were identified:    1,1‐DCE: decreasing trends at ES‐23 and ES‐30  TCE: decreasing trends at ES‐23, ES‐28, and RS‐15  Evaluation of natural attenuation processes at SSFL was performed in the Draft Site‐Wide Groundwater  Remedial Investigation Report, Santa Susana Field Laboratory, Ventura County, California (MWH, 2009) and  EN0317151003RDD 4-3 SECTION 4 DATA SUMMARY BY MEDIA accompanying documents. Chemical fate will be further evaluated in results from treatability studies  currently underway or being planned and in the CMS report. Further evaluations of contaminant transport  and fate may be conducted as outlined by the DTSC (DTSC, 2014).    4-4 EN0317151003RDD SECTION 5  Risk Assessment Summary This section presents a summary of the HHRA and ecological risk assessment (ERA) findings for the EEL RFI  site. The detailed HHRA and ERA findings are presented in Appendix E. All data applicable to the EEL RFI site  have been determined to be appropriate for use in risk assessments.   Additional data were collected by DOE and provided to Boeing after preparation of the EEL DSFR had  commenced; these data were not included in the risk assessments presented in Appendices E1 through E3  and are evaluated separately in Appendix E4.  5.1 Human Health Risk Assessment Findings A summary of the HHRA findings is presented in Table 5‐1. The detailed HHRA findings, including risk factors  and calculations, are presented in Appendix E1.  5.1.1 COPC/ROPC Selection Chemicals of potential concern (COPCs) are those chemicals that are carried through the HHRA  quantification process. Radionuclides carried through the HHRA process are referred to as radionuclides of  potential concern (ROPCs). The process for selection of COPCs/ROPCs for Chatsworth Formation  groundwater is described in Appendix C of the 5/9S DSFR (CH2M HILL, 2015a). Tables E1‐1 and E1‐2 of  Appendix E1 list the final human health COPCs identified for soil and soil vapor and the ROPCs identified for  soil at the EEL RFI site.   5.1.2 Exposure Assessment The exposure scenarios evaluated in the HHRA included the hypothetical future suburban residential and  future recreational user receptor groups. Each of these exposure scenarios was evaluated using the  exposure assumptions and methods described in the SRAM Rev. 2 Addendum (MWH, 2014c).   Since Boeing plans for the future use of its property as open space, the most likely future use of SSFL is for  recreational purposes, and recreational users are the most plausible future human receptors. Therefore, risk  estimates for future recreator scenarios are quantified in this HHRA. Boeing has also elected to assess  potential risks for a hypothetical suburban resident to provide conservative estimates for CMS planning.   The potential exposure scenarios considered include the following:   Hypothetical Suburban Resident – Soil Contact: Potential exposure of suburban residents to  constituents in soil down to 10 feet bgs4 by incidental ingestion, dermal contact, and inhalation of dust  and vapors   Hypothetical Suburban Resident – Indoor Air: Potential inhalation exposure of hypothetical suburban  residents to constituents volatilizing from soil vapor to indoors   Future Recreator: Potential exposure of future recreators to constituents in soil to 2 feet bgs by  incidental ingestion, dermal contact, and inhalation of dust and vapors   Risks associated with exposure of hypothetical future suburban residents to groundwater are identified at  the subarea scale and are described further in the 5/9S DSFR. The garden use exposure pathway scenario for  the hypothetical suburban resident was also considered; the risk calculations for this exposure scenario are  presented in Appendix E1.                                                               4 In accordance with the SRAM Rev. 2 Addendum, risk estimates for residential scenarios were estimated for both the 0 to 2 ft bgs and 0 to 10 ft bgs  depth intervals, and the interval exhibiting the higher risk is reported for each RFI site.  EN0317151003RDD 5-1 SECTION 5 RISK ASSESSMENT SUMMARY 5.1.3 Estimated Risks and Hazards The risk estimates for the following exposure scenarios were calculated for the EEL RFI site:    Hypothetical suburban residential scenario  Future recreational scenario  Each of these exposure scenarios was evaluated using the exposure assumptions and methods described in  the SRAM Rev. 2 Addendum (MWH, 2014c).  5.1.3.1 Hypothetical Suburban Residential Scenario Potential suburban residential exposure to COPCs in soil and soil vapor and ROPCs in soil was evaluated  under this scenario. The results are described by exposure medium in the following subsections, and  summarized in Tables E1‐3 and E1‐4.  Direct Contact with Soil  For the direct soil contact pathway for the hypothetical suburban residential exposure scenario, the total  site excess lifetime cancer risk (ELCR) is 4 x 10‐4 and the incremental risk is 3 x 10‐4, which is above the USEPA  target risk range of 1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of departure of 1 x 10‐6. The primary risk  driver to the incremental soil ELCR is arsenic (97 percent contribution), with minor contributions from  2,3,7,8‐TCDD TEQ and benzo(a)pyrene.  The total site hazard index (HI) for soil for this scenario is 2 and the incremental HI is also 2, which exceeds  the USEPA and DTSC threshold HI value of 1. Primary contributors to the incremental soil HI are 2,3,7,8‐ TCDD TEQ and arsenic. However, since 2,3,7,8‐TCDD TEQ and arsenic do not have the same critical toxic  endpoint and no individual chemical hazard quotient (HQ) exceeds 1, no unacceptable hazard is identified.  Indoor Air Pathway  For the indoor air pathway, the total site ELCR is 3 x 10‐5, which is within the USEPA target risk range of  1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of departure of 1 x 10‐6. The primary risk drivers are TCE (94  percent contribution) and benzene (6 percent contribution).   The total site HI for is 7 for this scenario, which exceeds the USEPA and DTSC threshold HI value of 1.  The primary contributor to the site HI is TCE (>99 percent contribution).  Exposure to Radionuclides in Soil  The risk estimates for ROPCs identified for soil were calculated separately from those associated with  COPCs. For the direct contact with soil pathway, the total site ELCR is 2 x 10‐7, which is below the USEPA  target risk range of 1 x 10‐6 to 1 x 10‐4 and below the DTSC point of departure of 1 x 10‐6.  5.1.3.2 Future Recreator Scenario Since Boeing plans for the future use of its property as open space, the most likely future human use of SSFL  is for recreational purposes. Potential recreational exposure to COPCs and ROPCs in soil is evaluated under  this scenario. The results are described in the following subsections.  Direct Contact with Soil  For the direct soil contact pathway, the total site ELCR is 1 x 10‐4, and the incremental risk is 7 x 10‐5, which  does not exceed the USEPA target risk range of 1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of departure  of 1 x 10‐6. The primary risk driver to the incremental soil ELCR is arsenic (96 percent contribution), with  minor contributions from 2,3,7,8‐TCDD TEQ and benzo(a)pyrene.   The total site HI for soil for this scenario is 0.4 and the incremental HI is 0.3, which is below the USEPA and  DTSC threshold HI value of 1.    5-2   EN0317151003RDD SECTION 5 RISK ASSESSMENT SUMMARY Exposure to Radionuclides in Soil  The risk estimates for ROPCs identified for soil were calculated separately from those associated with  COPCs. For the direct contact with soil pathway, the total site ELCR is 4 x 10‐8, which is below the USEPA  target risk range of 1 x 10‐6 to 1 x 10‐4 and below the DTSC point of departure of 1 x 10‐6.  5.1.4 Summary of Findings Chemicals/radionuclides of concern (COCs/ROCs) are those COPCs/ROPCs identified during the HHRA as  primary contributors posing unacceptable risk and, therefore, are retained for further evaluation during the  CMS. For this HHRA, COCs are identified for soil and soil vapor. COCs for groundwater are identified at the  subarea scale and are described further in the 5/9S DSFR. No ROCs are identified for soil at the EEL RFI site.  The following is a list of COCs identified for the hypothetical suburban residential exposure scenario at the  EEL RFI site based on the ELCR and HI estimates for each medium:   Soil: Arsenic, 2,3,7,8‐TCDD TEQ, and benzo(a)pyrene were identified as COCs for direct contact with soil  by hypothetical suburban residents.   Soil Vapor: TCE and benzene were identified COCs for inhalation of indoor air by hypothetical suburban  residents.  The following is a list of COCs identified for the future recreator exposure scenario at the EEL RFI site, based  on the ELCR and HI estimates:   Soil: Arsenic, 2,3,7,8‐TCDD TEQ, and benzo(a)pyrene were identified as COCs for direct contact with soil  by future recreators.  An additional evaluation was conducted to determine the potential for localized areas where higher  constituent concentrations (that is, potential hot spots) could occur and to determine whether these may  represent additional areas that warrant evaluation in the CMS. As indicated in Attachment 1 of Appendix E1,  the COPCs identified as potential soil hot‐spot chemicals at the EEL RFI site include arsenic, 2,3,7,8‐TCDD  TEQ and benzo(a)pyrene. Since these COPCs are already identified for evaluation in the CMS based on the  HHRA results, no additional chemicals or areas are identified based on this hot‐spot evaluation.  5.2 Ecological Risk Assessment Findings A summary of the ERA findings is presented in Table 5‐2. The detailed ERA findings, including risk factors and  calculations, is presented in Appendix E2.  5.2.1 CPEC/RPEC Selection Chemicals of potential ecological concern (CPECs) and radionuclides of potential ecological concern (RPECs)  were identified from existing soil and soil vapor data that were evaluated according to the SRAM Rev. 2  Addendum (MWH, 2014c). Table E2‐2 of Appendix E2 lists the CPECs identified for soil and soil vapor at the  EEL RFI site. Table E2‐12 of Appendix E2 lists the RPECs at the EEL RFI site.   5.2.2 Exposure Assessment Exposure scenarios and receptor exposure factors for the SSFL were evaluated and presented in Appendix C  of the SRAM Rev. 2 Addendum (MWH, 2014c). The potential exposure scenarios evaluated for the EEL RFI  site are summarized below:   Birds: Potential exposure for birds (hermit thrush) includes incidental ingestion of soil (0 to 2 feet bgs)  and food‐chain uptake (ingestion of food sources that may have bioaccumulated CPECs).    Mammals: Potential exposure for small mammals (deer mouse) includes the following:  EN0317151003RDD 5-3 SECTION 5 RISK ASSESSMENT SUMMARY  Soil: Exposure via incidental ingestion of soil and food‐chain uptake (ingestion of food sources that  may have bioaccumulated CPECs). Soil depth interval with maximum potential risk is used and can  include 0 to 2 feet bgs, 0 to 4 feet bgs, or 0 to 6 feet bgs.    Soil Vapor: Exposure through inhalation of soil vapor for burrowing mammals (deer mouse) is  evaluated for CPECs in soil vapor (0 to 6 feet bgs).  Potential exposures for terrestrial plants and soil invertebrates were also evaluated, but were not used as  the sole determinant for CMS recommendation (that is, chemicals with CPECs HQs>1 for plants or  invertebrates but not for other receptors were not retained as COECs).  5.2.3 Estimated Risks and Hazards Potential risks from CPECs in soil were evaluated for exposures by birds and mammals (incidental ingestion  and food‐chain uptake). Receptor‐specific risk estimates, including HQs and HIs (where applicable), are  presented in Appendix E2. A summary of all HQs and chemical group HIs for soil exposures are presented in  Attachment 1 of Appendix E2.   CPECs with HQs exceeding 1 at the Low EcoRBSL for at least one receptor are summarized below. Those with  HQs exceeding 1 at the High EcoRBSL are indicated in bold. Results are for measured data unless otherwise  indicated (that is, “extrapolated” PCB TEQs and “sample quantitation limit” (SQL) for nondetect chemicals  retained as CPECs).    Hermit thrush: dioxins and furans TEQ for birds, 4,4’‐DDT, PCB TEQ for birds (extrapolated)  Deer mouse: antimony, arsenic, Aroclor‐1248 (SQL), dioxins and furans TEQ for mammals, 2‐methyl‐4‐ chlorophenoxyacetic acid (MCPA), PCB TEQ for mammals (extrapolated)  Chemical group HIs were calculated for birds and mammals for aroclors, PAHs (high and low), and  organochlorine pesticides. The HQ and HI for dioxins and furans are the same value because the TEQ is  already a summation of dioxin and furan congeners. HIs exceeded 1 for the following (those exceeding 1 at  the High EcoRBSL are indicated in bold):    Hermit thrush: aroclors, dioxins and furans TEQ for birds, and organochlorine pesticides  Deer mouse: dioxins and furans TEQ for mammals  Incremental risks were calculated for the CPECs with site HQs exceeding 1 (listed above) where background  data were available and are presented in Appendix E2. CPECs with incremental HQs exceeding 1 are  summarized below with those exceeding at the High EcoRBSL noted in bold:    Hermit thrush: PCB TEQ for birds (extrapolated).  Deer mouse: antimony, arsenic, dioxins and furans TEQ for mammals, MCPA, PCB TEQ for mammals  (extrapolated). A background BTV was not available to calculate incremental risks for Aroclor‐1248).   Dioxins and furans TEQ for mammals was the only COEC identified for the EEL RFI site. Remaining CPECs  with HQs exceeding 1 were not retained as COECs based on weight‐of‐evidence, as discussed below:   Antimony, arsenic, hexavalent chromium, MCPA, and 4,4’‐DDT were not retained as COECs. Incremental  risk HQs did not exceed 1 at the High EcoRBSL, and there were no potential hot spots identified.   Dioxins and furans TEQ for birds was not retained as a COEC. Site and incremental risk HQs did not  exceed 1 at the High EcoRBSL, and potential hot spots were not identified. Dioxins and furans TEQ for  mammals was retained as a COEC as noted above. Toxicity to birds differs from mammals, and it is not  uncommon to show unacceptable risks to one group and not the other.    Aroclor‐1248 was not retained as a COEC. This analyte was identified as a CPEC as a result of the SQL  screen (Table 6 in Attachment 1 of Appendix E2). Other detected aroclors did not show unacceptable  risks to ecological receptors. Potential for risks from Aroclor‐1248 were considered low.  5-4 EN0317151003RDD SECTION 5 RISK ASSESSMENT SUMMARY  PCB TEQs (birds and mammals) were not retained as COECs. This constituent was extrapolated from  Aroclor‐1254 and ‐1260 results. As noted above, dioxins and furans TEQ for mammals was retained as a  COEC. There were no unacceptable risks to ecological receptors from aroclors.  5.2.4 Summary of Findings Potential risks from chemicals and radionuclides were evaluated for terrestrial receptors, including birds  (hermit thrush) and mammals (deer mouse). COECs and ROECs are those CPECs/RPECs identified during the  ERA as primary contributors posing unacceptable risk and are therefore retained for further evaluation  during the CMS. For this ERA, the following risk drivers were identified:     Soil COECs: dioxins and furans TEQ for mammals  Soil vapor COECs: none  Soil ROECs: none  An additional evaluation was conducted to determine the potential for localized areas where higher  constituent concentrations (that is, potential hot spots) could occur. The maximum detected concentration  of dioxins and furans TEQ for mammals exceeded 10 times the High EcoRBSL for the most sensitive receptor  and may indicate potential hot spots.  5.3 Uncertainties Uncertainties associated with the results of the HHRA and ERA are a function of both the “state of the  practice” of risk assessment in general and uncertainty factors specific to an RFI site. The EEL RFI site HHRA  and ERA are subject to uncertainty with regard to a variety of factors that include:       Environmental sampling and analysis  Fate and transport estimation  Exposure assessment  Toxicity assessment  Risk characterization  Detailed uncertainty analyses are presented in Appendixes E1 and E2. Appendix E3 provides the results of  the non‐CMS area evaluations for human health and ecological receptors for the EEL RFI site.       EN0317151003RDD 5-5 SECTION 6  CMS and NFA Recommendations This section presents a summary of the CMS and NFA recommendations for the EEL RFI site.   6.1 CMS Recommendations Areas are recommended for CMS for the following media:   Soil and soil vapor CMS areas are based on the human health and ecological risk assessments provided  in Appendix E, including the separate analysis of additional DOE data provided in Appendix E4.    Vadose zone CMS areas are based on the vadose zone to groundwater transport modeling presented in  Appendix C, including the separate analysis of additional DOE data provided in Attachment C‐5 to  Appendix C.   Groundwater COCs recommended for CMS are based on the evaluation of the source zone, nature and  extent, and fate and transport of chemicals in groundwater presented in Appendix D.  Table 6‐1 presents a summary of the CMS recommendations and risk drivers for all media. Figure 6‐1  presents the areas recommended for CMS. The approach and basis for CMS area identification is presented  in the 5/9S DSFR (CH2M HILL, 2015a). The size and shape of the areas recommended for CMS are based on  professional judgement that includes an evaluation of factors such as media, site features and topography,  data distribution, and concentration magnitudes and gradients. Where additional site‐specific information  was considered in delineating CMS areas, this information is presented under Study Question #5 of Table  4‐1. The subarea‐scale VI pathway evaluation supporting these CMS recommendations for the EEL RFI site is  presented in the 5/9S DSFR. Human health risks associated with the hypothetical domestic use of  groundwater are evaluated at the subarea scale and are presented in Appendix C of the 5/9S DSFR.   The vadose zone CMS areas and locations include soil, soil vapor, and rock pore water sample locations that  are interpreted to pose a potential threat to groundwater based on the data evaluation and transport  modeling results presented in Appendix C. The criteria used to determine CMS areas and locations include  consideration of chemical concentrations relative to the vadose zone screening values and background  ranges identified in the soil background study (URS, 2012), transport modeling results, spatial data  distribution, site features such as drainages and faults, and historical activities. Using these criteria, CMS  areas are drawn where data are sufficient to delineate a boundary around locations with exceedances of  vadose zone concentrations that are protective of groundwater as determined by the modeling. For cases  where there are isolated detections of chemicals in exceedance of vadose zone concentrations protective of  groundwater and the data are not sufficient to delineate an area, the individual sample location is displayed  as a CMS location.  The CMS areas described below and in Table 6‐1 and on Figure 6‐1 will be evaluated further during the  upcoming CMS evaluation for the Boeing RFI subareas.   6.1.1 Soil As presented in Table 6‐1 and shown on Figure 6‐1, nine areas are recommended for CMS for soil based on  the findings of the HHRA, ERA, and the separate DOE data evaluation presented in Appendix E this report.  The nine areas recommended for CMS and their chemical risk drivers for soil are:       EEL‐CMS‐S1 (arsenic and dioxins and furans TEQ for mammals)  EEL‐CMS‐S2 (arsenic)  EEL‐CMS‐S3 (arsenic)  EEL‐CMS‐S4 (benzo(a)pyrene)  EEL‐CMS‐S5 (dioxins and furans TEQ for mammals)  EN0317151003RDD 6-1 SECTION 6 CMS AND NFA RECOMMENDATIONS     EEL‐CMS‐S6 (dioxins and furans TEQ for mammals)  EEL‐CMS‐S7 (dioxins and furans TEQ for mammals)  EEL‐CMS‐S8 (dioxins and furans TEQ for mammals)  EEL‐CMS‐S9 (dioxins and furans TEQ for mammals)  6.1.2 Soil Vapor As presented in Table 6‐1 and shown on Figure 6‐1, two areas are recommended for CMS for soil vapor  based on the findings of the HHRA presented in this report. The two areas recommended for CMS and their  chemical risk drivers for soil vapor are:    EEL‐CMS‐SV1 (TCE)  EEL‐CMS‐SV2 (TCE and benzene)   6.1.3 Vadose Zone As presented in Table 6‐1 and shown on Figure 6‐1, the following areas and locations are recommended for  CMS for the vadose zone because they pose a potential future threat to groundwater based on evaluations  presented in Appendix C:   Vadose zone CMS areas:  ‐ EEL‐CMS‐VZ1 (TCE, perchlorate)  ‐ EEL‐CMS‐VZ2 (TCE, 2,4‐dichlorophenoxybutyric acid and heptachlor epoxide)   Vadose zone CMS locations:  ‐ ELBS2000 (beta‐BHC, heptachlor, MCPA)  ‐ SL‐143‐SA5C (perchlorate, MCPA)  ‐ ELBS2035 (nitrate‐NO3)  The vadose zone CMS location SL‐143‐SA5C was included based on a qualitative analysis performed on  additional data collected at the site by DOE. The qualitative analysis is presented in Attachment C‐5 of  Appendix C.  The transport modeling conducted for the vadose zone to groundwater evaluation produced highly  conservative results for chemicals that readily degrade because the transport model does not account for  biodegradation. Thus, it is recommended that the vadose zone CMS areas and locations be revisited during  the CMS to consider natural attenuation processes.  Vadose zone to groundwater transport modeling predictions identified seven chemicals in the vadose zone  not detected in groundwater that will impact groundwater at concentrations above their GCLs during the  100‐year simulation based on their maximum soil concentrations measured at the EEL RFI site (Appendix C).  These chemicals, listed below, are recommended for groundwater monitoring every 5 years to evaluate the  potential presence of these chemicals in groundwater:              6-2 Perchlorate  2,4‐dichlorophenoxybutyric acid  MCPA  Beta‐benzene hexachloride   Heptachlor  Heptachlor epoxide  Barium  Mercury  Silver  Sodium  Fluoride  Nitrate‐NO3  EN0317151003RDD SECTION 6 CMS AND NFA RECOMMENDATIONS 6.1.4 Groundwater and Seeps Findings of the groundwater evaluation for the EEL RFI site indicate five chemicals sourced from the EEL RFI  site are present in groundwater above GCLs: cis‐1,2‐DCE, TCE, diesel‐range organics, manganese, and  cadmium. This evaluation is presented as Appendix D of this document. Based on evaluation of the source  zone, nature and extent, and fate and transport of chemicals in groundwater at the EEL RFI site, the  following chemicals are recommended for CMS assessment in groundwater:    cis‐1,2‐DCE  TCE  The following chemicals are recommended for additional monitoring at the specified wells because data  were not sufficient to make recommendations for CMS or NFA:     Cadmium at PZ‐050  Manganese at PZ‐050   Diesel‐range organics at PZ‐050 and ES‐30  If these wells continue to be dry or contain insufficient water for sampling, alternate locations will be  recommended for sampling, or installation of replacement wells will be considered.  6.2 NFA Recommendations Soil, soil vapor, and vadose zone bedrock in portions of the EEL RFI site outside of the recommended CMS  areas presented on Figure 6‐1 are recommended for NFA.5 The portions of the site outside of CMS areas do  not pose unacceptable risk or hazards to the hypothetical suburban resident or small home range ecological  receptors, nor do they pose a threat to groundwater quality. Potential releases in the areas recommended  for NFA have been investigated using a robust, systematic approach to identify and characterize potential  sources of releases from historical site operations. The NFA recommendations for the EEL RFI site are  supported by the weight‐of‐evidence documentation presented in Table 3‐1 that documents the breadth of  the sources of information reviewed and evaluated, by the results of the HHRA and ERA presented in  Appendix E, and by the evaluation of nature and extent and contaminant transport evaluations inclusive of  all media as presented in Tables 4‐1 and 4‐4.   As discussed above and shown on Figure 4‐7, groundwater underlying a majority of the EEL RFI site is  impacted by VOCs based on groundwater source zone and plume characterization evaluations, and is  recommended for CMS evaluation.                                                                  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Ogden Environmental and Energy Services Co., Inc. (Ogden). 1996. RCRA Facility Investigation Work Plan  Addendum, Santa Susana Field Laboratory, Ventura County, California. September.  Ogden Environmental and Energy Services Co., Inc. (Ogden). 2000. RCRA Facility Investigation Work Plan  Addendum Amendment, Santa Susana Field Laboratory, Ventura County, California. June.  Science Applications International Corporation (SAIC). 1991. Final RCRA Facility Assessment Report for  Rockwell International Corporation, Rocketdyne Division, Santa Susana Field Laboratory, Ventura County,  California. Prepared for USEPA Region IX. July.  Science Applications International Corporation (SAIC). 1994. Final RCRA Facility Assessment Report for  Rockwell International Corporation, Rocketdyne Division; Santa Susana Field Laboratory, Ventura County,  California. May. HDMSE00008191.  United States Environmental Protection Agency (USEPA). 2009. “National Secondary Drinking Water  Regulations,” EPA 816‐F‐09‐004. May.  United States Bureau of Reclamation. 1998. Engineering Geology Field Manual. Second Edition.   URS. 2012. Chemical Soil Background Study Report, Santa Susana Field Laboratory, Ventura County,  California. December.  EN0317151003RDD 7-3 SECTION 8  Glossary of Terms Boeing RFI Subarea: The portions of land that are not subject to the DOE or NASA AOCs were organized into  nine Boeing RFI subareas to complete the RFI in accordance with the 2007 Consent Order. Each Boeing RFI  subarea consists of zero to four RFI sites and surrounding land.  Characterization Level: These are the screening levels applicable to soil, soil vapor, sediment, and surface  water. Characterization levels are based on the higher of the 1) Combined Strata 95‐95 Upper Tolerance  Limit background threshold values (for chemicals that have such values) and 2) lowest of applicable  Suburban Residential RBSLs and Ecological Low RBSLs. Characterization levels for some chemicals are  established as the method reporting limit that can be achieved by multiple laboratories if achieving the risk‐  or background level‐based characterization level is deemed technically limited and/or infeasible.   Chemical Use Area (CUA): CUAs are areas of known or potential chemical use, storage, handling, or disposal  within each of the RFI/RI reporting areas.  CUA Cluster: A CUA cluster is a grouping of one or more CUAs that are combined based on similarities in  geographic proximity, operational history, lithologic features, analytical parameters, previous CMS  recommendations, and locations of dense nonaqueous‐phase liquid sources/releases. CUA clusters consist  of one or more CUAs and include the full extent of identified impacts above characterization levels.  Conditional No Further Action recommendation: This is an NFA recommendation based on current site  information and weight‐of‐evidence data that is considered conditional pending collection and evaluation of  additional groundwater data.   Dioxins and Furans: Dioxins and furans are referenced as “2,3,7,8‐TCDD TEQ” in human health risk  assessment terms. Dioxins and furans are referenced as “dioxins and furans TEQ for mammals” or “dioxins  and furans TEQ for birds” in ecological risk assessment terms. Dioxins are referenced as “dioxins and furans”  when the nature and extent of the analytical group is referenced.  Plume: A plume is a contiguous area of groundwater contamination resulting from one or more vadose zone  sources. Plume extent is bounded laterally by concentrations at or below the required characterization  levels and bounded vertically by concentrations at or below 10 times the required characterization levels.  RCRA Facility Investigation site (RFI site): A RFI site is a group of Solid Waste Management Units or Areas of  Conern identified at the SSFL as part of several comprehensive evaluations by regulatory agencies. These  evaluations occurred in 1989, 1996, and 2000, and considered current and historical site operations and  existing environmental data. As a result of these reviews, a total of 135 Solid Waste Management Units and  Areas of Concern were identified at the SSFL. Of these, 29 are either closed or being closed as part of other  environmental programs at the facility, or do not require further action during the RFI. The remaining 106  Solid Waste Management Units and Areas of Concern are being evaluated in the Surficial Media OU RFI, and  have been grouped into 51 RFI sites based on similarity of location, chemicals used, and historical operations  (SAIC, 1991) (Ogden Environmental and Energy Services Co., Inc. [Ogden], 1996) (Ogden, 2000).Sediment:  Sediment is the material at the bottom of perennial surface water features that does not include soil in  ephemeral streambeds.  Surface Water: Considered as the following:    “Surface water drainage,” such as sheet flow or channel flow, where surface water runoff could cause  migration of surface soil. Evaluated as a potential migration pathway from a CUA.   “Surface water features,” water bodies, such as ponds, where water accumulates. Evaluated as a  potential source of contamination under the Surficial Media Operable Unit RFI.   EN0317151003RDD 8-1 SECTION 8 GLOSSARY OF TERMS Vadose Zone: This is the area of unsaturated soil (alluvium), weathered bedrock, and unweathered bedrock  present between the ground surface and the water table.  Weathered Bedrock: Weathered bedrock at SSFL is considered the lithological profile of rock that meets the  definition of W7 through W1, as described in Table 4‐4 of the United States Bureau of Reclamation  Engineering Geology Field Manual (United States Bureau of Reclamation, 1998), and above the first‐ encountered saturated zone. 8-2 EN0317151003RDD Tables TABLE 3‐1 Assessment Elements for Identification of Potential Contamination Sources and Weight‐of‐Evidence Documentation for CMS and NFA Recommendations for the EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Activities to Support NFA Area Recommendations for the  Assessment and documentation supporting recommendation that no release or potential release of any chemical previously used, stored, handled or disposed was identified within the EEL RFI site, other than the  CUAs identified in EEL RFI site media‐specific evaluations SMOUa Review of all available historical RCRA Facility Investigation related reports and documents. Method 1: SSFL Document and Record Review RCRA Facility Assessment RFA (1989 ‐ 1994) historical and current operational chemical use information was reviewed, a site inspection was performed, and previous sampling data were evaluated to determine the likelihood of a potential  release to environmental media. One hundred and twenty‐five areas of SSFL that used, stored, or handled hazardous waste were identified for designation as SWMUs or AOCs by the USEPA. During the RFA, one SWMU  was identified at the EEL RFI site: Building 3268 and Building 3271 (SWMU 6.9) (Science Applications International Corporation, 1991).  RFI Program Report Subsequent to the RFA, 10 additional AOCs were identified during the SSFL RFI Program Report preparation, for a total of 135 SWMUs and AOCs at the entire SSFL. These 135 SWMUs and AOCs were grouped into 51 RFI  sites. Boeing, DOE, NASA, and DTSC subdivided the SSFL into 11 RFI groups for the purposes of RFI reporting work activities, each containing zero to 17 RFI sites. EEL was grouped with other RFI sites in the RFI Program  Report to form Group 5. No additional SWMUs or AOCs were identified in the EEL RFI site during this process (MWH, 2004).    2008 EEL RFI Report  DTSC and Stakeholder Comments on this Report The 2008 EEL RFI Report considered all historical reporting and documentation available at the time of report preparation. Seventy‐nine soil samples and 23 soil vapor samples were collected from the EEL RFI site  between February 1993 and May 2008. The analytical results for all these samples were included in the 2008 EEL RFI Report and were used to prepare CMS and NFA recommendations for the EEL RFI site. Eight CUAs  were identified in the 2008 EEL RFI Report (CH2M HILL, 2008), and these serve as the baseline compilation of CUAs for the EEL RFI site that are evaluated and expanded upon during implementation of the DQO  evaluation process.   DTSC and stakeholder comments on the 2008 EEL RFI Report are considered under the context of the comprehensive DQO process. No new release or potential release was identified as a result of DTSC's review of the  EEL RFI Report. Responses to DTSC comments on the 2008 EEL RFI Report were provided as Appendix B of the Addendum to Master RFI Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana  Field Laboratory, Ventura County, California  (CH2M HILL, 2013a). RFI‐relevant information derived from DTSC comments on the 2008 EEL RFI Report have been incorporated into the applicable record review, sitewide  inventory and inspection, site‐specific inspection, and chemical migration assessment activities presented in this table. Sitewide Groundwater Remedial Investigation Report The Sitewide Groundwater Remedial Investigation Report (MWH, 2009) presents an assessment of the nature and extent of SSFL site‐related chemicals in groundwater and the vadose zone bedrock. The Groundwater RI Report was reviewed to identify information relevant to the EEL SMOU. The report indicates that impacted groundwater has been found in samples collected from wells within the footprint of the EEL RFI site. The  chemicals detected in groundwater samples collected from these wells are consistent with chemicals detected in surficial media samples or is attributed to sources at other RFI sites. Based on the above, no new releases or potential releases were identified at the EEL RFI site based on the review of this report.   Review of Historical Documentation   Review of historical documentation was performed, including but not limited to, reports, maps, inventories, spill records, notes, and correspondence to identify areas of chemical use not already identified during the  prior RFA or RFI activities. Approximately 70,000 historical documents related to Group 5 were reviewed for identification of information potentially relevant to the Boeing SSFL RFI, and findings were included in the  2008 Group 5 RFI Report. Electronic copies of these historical documents were previously provided to DTSC on external hard drives. Subsequently, additional historical documents that became available were reviewed  using the same process to identify RFI‐relevant information. Electronic versions of these documents were provided to DTSC in 2013. For completeness, Boeing is submitting a separate deliverable to DTSC that will  include electronic copies of the comprehensive set of historical documents identified to contain information relevant to site features, historical operations, and chemical and radiological uses for the Boeing RFI subareas  (Boeing, pending).  The review of the additional historical documentation resulted in the identification of new releases or potential releases beyond those presented in the 2008 EEL RFI Report. These releases or potential releases were  presented in Table A‐2 of the Addendum to Master RFI Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2013a) and Table A‐2 of  the Addendum to Master RFI Data Gap Work Plan ‐ Second Iteration, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2014a). The potential releases  documented in those work plan addenda that could pose a risk to human health or the environment were investigated in accordance with the comprehensive DQO process. No other potential releases have been  identified at the EEL RFI site as a result of review of historic documentation. Method 2: SSFL Sitewide Inventories Building Inventory and Feature Survey EN0317151003RDD Compilation and evaluation of sitewide inventories of infrastructure or features with potential chemical storage, distribution, use, or disposal history The building feature inventory and survey was performed at the EEL RFI site in 2008 to systematically identify the location and condition of all existing building features that potentially could have been a source of a  chemical release to environmental media. All tasks identified in the Building Feature Survey standard operating procedure (MWH and CH2M HILL, 2008a) have been reviewed, and all available and relevant information  was documented in the EEL building feature documentation logs. These logs were originally provided as an attachment to the 2008 EEL RFI Report and also provided with the Central Key Document Repository  deliverable to DTSC in April 2011 (and subsequently in May 2012). Five building features where a chemical release to environmental media may have occurred were identified during the building feature inventory and  survey for the EEL RFI site. The five building features (3268‐002, 3268‐004, 3268‐006, 3268‐010, and 3271‐001) had nearby samples to characterize soil near the features. Soil and soil vapor sample results from these  locations were evaluated in accordance with the DQO evaluation process. No other new releases or potential releases were identified during the building inventory and feature survey for the EEL RFI site.     PAGE 1 OF 5 TABLE 3‐1 Assessment Elements for Identification of Potential Contamination Sources and Weight‐of‐Evidence Documentation for CMS and NFA Recommendations for the EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Activities to Support NFA Area Recommendations for the  Assessment and documentation supporting recommendation that no release or potential release of any chemical previously used, stored, handled or disposed was identified within the EEL RFI site, other than the  CUAs identified in EEL RFI site media‐specific evaluations SMOUa Tank Inventory A SSFL sitewide Tank Inventory was prepared by Boeing, DOE, and NASA. This inventory identifies all known information regarding the location, size, composition, contents, use period, and regulatory status of all  underground storage tanks, aboveground storage tanks, and undetermined tanks. Eight new undetermined tanks with unknown contents was identified at the EEL RFI site during the historical document review and have been added to the tank inventory. These tanks are addressed in the review of historic documentation section in Table A‐2 of the Addendum to Master RFI Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI  Site, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2013a) and Table A‐2 of the Addendum to Master RFI Data Gap Work Plan ‐ Second Iteration, Boeing RFI Subarea 5/9 South, EEL RFI Site,  Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2014a). The documentation for the entire Boeing SSFL tank inventory was provided with the Central Key Document Repository deliverable to  DTSC in April 2011 (and subsequently in May 2012) and an updated version of the Boeing SSFL tank inventory will be provided to DTSC in the future.  No other tanks were identified at the EEL RFI site during the sitewide  tank inventory compilation.     Sewer System Survey The SSFL sitewide sewer system survey was performed in 2008 and 2009 to visually inspect sewer manholes and pipeline inlets and outlets and to identify manholes that are in poor condition and may have resulted in  impacts to environmental media. CH2M HILL inspected the 33 sanitary sewer system manholes located in Group 5 in August 2008. A small section of the sewer pipeline runs through the EEL RFI site, but was not  connected to any site buildings. There are two manholes located in the EEL RFI site and were inspected. These manholes were observed to be active and intact. No sediment was observed inside these manholes at the  time of the inspection. No fractures or deterioration of the concrete manhole structure, including the inlet and outlet pipelines, was observed. Sanitary sewer inputs, segments, and depths were compiled and presented  in the Sanitary Sewer System Assessment for Boeing RFI Subareas, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2015a). Leach fields were also reviewed, and it was determined that no leach  fields existed at the EEL RFI site. An evaluation of the sanitary sewer system and nearby soil and soil vapor data within the EEL RFI site are presented in Section 4.0 of this DSFR. As presented in Section 4.0, there doesn't  appear to have been releases from the sanitary sewer system at the EEL RFI site that resulted in concentrations that exceed characterization levels. No other features were identified during the sewer system survey at  the EEL RFI site.  Reclaimed Water System Inventory A comprehensive sitewide evaluation was performed by Boeing, DOE, and NASA to identify and document the locations and operational history of all features associated with the reclaimed water system. The  documentation for the Boeing SSFL reclaimed water system was provided with the Central Key Document Repository deliverable to DTSC in May 2012. Spray fields and pipelines associated with the reclaimed water  system were identified in the western and eastern portions of the EEL RFI site during the 2010/2011 reclaimed water conveyance system inventory activities. The Reclaimed Water System Assessment for Boeing RFI  Subareas, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2015b) presents a summary of the components of the reclaimed water portion of the water conveyance system, potential inputs to the  system, and potential chemicals and radionuclides that may be associated with the system. As presented in Section 4.0, analytical data collected from sprayfield areas and along pipelines within the EEL RFI site were  evaluated for the chemicals that are associated with reclaimed water. Semivolatile organic compounds and 4,4’‐DDT results may be associated with potential releases from the sprayfields and the western and eastern  sprayfields at the EEL RFI site, which have been identified as CUAs 15 and 16, respectively. A small portion of the reclaimed water pipeline in the EEL RFI site that was investigated as a portion of Potential CUA B was  excluded from CUA 16 on the basis that screening‐level data do not indicate that releases above the characterization levels from this pipeline section have occurred. Major features of the reclaimed water system at the EEL RFI site have been investigated for the potential analytes identified in Table 2 of the DQO report (CH2M HILL 2013b). Minor features such as pipelines and  drainages of the reclaimed water system have an adequate number of samples in the vicinity of these features to fully characterize them. No other features were identified during the reclaimed water system inventory  review at the EEL RFI site. Pipelines Wrapped with Mastic Tape Documentation A comprehensive sitewide evaluation was performed by Boeing, DOE, and NASA to identify and document the locations of natural gas pipelines wrapped with mastic tape (that potentially contain PCBs, asbestos, and  semivolatile organic compounds). A summary of the natural gas pipeline system at SSFL was provided with the Central Key Document Repository deliverable to DTSC in May 2012. In addition, other pipelines wrapped  with mastic tape have been identified elsewhere at SSFL. No natural gas pipelines wrapped with mastic tape have been identified within the EEL RFI site, as documented in the Natural Gas Pipeline GIS Feature Class  Technical Memorandum (MWH, 2012). In addition, no other types of pipelines wrapped with mastic tape have been identified at the EEL RFI site. Primary Fuel‐oil and Chemical Pipeline Inventory A review of available documentation has been performed. No fuel‐oil or chemical pipelines extending within, to, or from the EEL RFI site were identified.    GIS Gold Copy Data Management Tool The GIS Gold Copy Data Management Tool is a comprehensive GIS and analytical database that was compiled for SSFL and contains current and complete Boeing, NASA, and DOE chemical and radiological data for  surficial media and groundwater. The GIS Gold Copy Data Management Tool was submitted to DTSC initially in April 2011 and an updated version of the tool was subsequently submitted to DTSC in May 2012. This tool  was reviewed to identify any new features potentially associated with a release to environmental media that are not included in the 2008 EEL RFI Report and not identified elsewhere in this table. No other new features  potentially associated with a release in the EEL RFI site were identified through this process. Method 3: SSFL Sitewide Inspections Debris Survey and Sampling SSFL sitewide comprehensive inspections and documentation  Boeing, DOE, and NASA performed a sitewide debris survey in 2008 and 2009 to systematically identify surficial evidence of solid waste disposal through visual inspections of the SSFL. The debris survey was conducted  on 50‐foot transects across all of SSFL to document the types and locations of debris. The survey was performed in accordance with the Onsite Debris Survey and Sampling Methodology standard operating procedure  (CH2M HILL and MWH, 2008b). No debris areas were identified at the EEL RFI site.     A sitewide survey of biological and ecological site conditions was performed in 2008. The results of the survey were mapped and included in the Boeing Group 5 RFI Report. No new releases or potential releases  conditions were identified at the EEL RFI site during the biological survey. Biological Survey and Mapping EN0317151003RDD PAGE 2 OF 5 TABLE 3‐1 Assessment Elements for Identification of Potential Contamination Sources and Weight‐of‐Evidence Documentation for CMS and NFA Recommendations for the EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Activities to Support NFA Area Recommendations for the  Assessment and documentation supporting recommendation that no release or potential release of any chemical previously used, stored, handled or disposed was identified within the EEL RFI site, other than the  CUAs identified in EEL RFI site media‐specific evaluations SMOUa Aerial Photograph Review Review of historical aerial photographs was performed, commencing in 1997 (USEPA) and continuing through 2011 (Boeing, DOE, and NASA) to identify areas of chemical use not previously identified. Boeing, DOE, and  NASA reviewed historical aerial photographs representing 17 photo coverage years that span the lifecycle of SSFL facility operations, from 1953 to 2005. Features identified in the aerial photograph review were  documented in GIS. The documentation for the entire Boeing SSFL aerial photograph review was provided with the GIS Gold Copy Data Management Tool to DTSC in May 2012. New features in the EEL RFI site were  identified during the aerial photograph review as documented in Table A‐2 of the Addendum to Master RFI Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura  County, California  (CH2M HILL, 2013a). Potential CUAs were identified for potential releases outside existing CUAs and were investigated in accordance with the comprehensive DQO process. Portions of these Potential  CUAs were not converted to CUAs based on the screening‐level sample results. Information on the Potential CUAs at EEL are presented in Table 3‐2 and Section 4.0 of the EEL DSFR. No other potential releases have  been identified at the EEL RFI site as a result of review of aerial photographs. Method 4: EEL RFI Site Inspections Topography and Physical Accessibility EEL RFI site‐specific inspections and documentation  The topography at the EEL RFI site was evaluated to identify areas of the site for which historic chemical use, storage, handling, or disposal activities would have been prohibitively difficult. No areas of the EEL RFI site  were identified as being prohibitively difficult to access. Therefore, all portions of the EEL RFI site were subject to evaluations regarding the historic use, storage, handling, or disposal of chemicals. Proximity to Roadways and Operations The roadways located within the EEL RFI site were evaluated in the context of the Field Sampling Methodologies for CUA or CNFA Determination for the SMOU (Table 2 of the Comprehensive DQO Report). No releases  or potential releases were identified based on an evaluation of operations in proximity to roadways at the EEL RFI site.  A geophysical survey was performed at the EEL RFI site in 2010. Anomalies of interest mostly include buried conduits with occasional unknown features. The unknown subsurface features identified during the  geophysical survey were further evaluated during biased grid sampling. The results of that sampling, which was also intended to address tanks with unknown locations identified during the historical document review  and soil disturbance features identified during the aerial photograph review, did not reveal areas of EEL RFI site where subsurface features are likely to have resulted in releases to the environment.  Geophysical Survey Demolition Documentation and Sampling Field oversight was conducted during demolition of existing buildings and structures at the EEL RFI Site in 2012 to identify locations of potential impacts to environmental media beneath the buildings and structures  (through observation, field monitoring, and sample collection and chemical analysis). No impacted soil was observed during the building demolition activities and therefore no samples were collected. Portions of an  underground sewer pipeline remain in place following demolition activities. The remaining portions of the pipeline are approximately 95 feet of 8‐inch‐diameter vitreous clay pipe and 25 feet of 4‐inch‐diameter steel  pipe located southwest of the EEL RFI site under the road near the southwest manhole, MH‐D2 (which remains), and approximately 90 feet of 10‐inch‐diameter vitreous clay pipe along the eastern boundary of the EEL  RFI site, north of the manhole along the eastern boundary, MH‐A1,D1 (which remains). These portions of the pipeline will be removed during future demolition activities, and sampling will be performed, if warranted,  based on observations during removal. An 80‐foot portion of a surface water treatment pipeline also remains in place in the northeast corner of the EEL RFI site. This single‐walled pipeline was installed recently  (2010/2011), and there is no evidence of releases of treated surface water from this pipeline. No new releases or potential releases have been identified at the EEL RFI site based on demolition activities performed to  date. Interim Removal Actions As part of the DTSC‐approved 1993 Accelerated Corrective Action Work Plan (Appendix I of the Current Conditions Report; ICF, 1993), an interim removal action for TPH was performed in 1993 at CUA 8 consisting of  excavation of approximately 2‐3 cubic yards of soil near the concrete pad where drums were stored. Aside from this interim removal action, no other interim removal actions have been performed at the EEL RFI site. Recent Data Gap Field Sampling Observations Method 5: Chemical Migration Assessment Vapor Intrusion Pathway Evaluation No items were noted (such as staining, odors on soil samples) during field activities post 2008 RFI report field sampling that would indicate a potential chemical release.  Evaluation of potential chemical migration from any CUA to EEL RFI site areas thought to be unimpacted (EEL RFI site NFA areas) The vapor intrusion pathway was evaluated in accordance with Appendix A of the Comprehensive DQO Report: Recommended Approach for Assessing the Vapor Intrusion Pathway, Boeing RCRA Facility Investigation  Project, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2013c). The Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2015c) presents an evaluation of the vapor intrusion migration pathway and recommendations for filling data gaps to support future evaluation of the vapor intrusion pathway for each RFI site in Boeing RFI  Subarea 5/9 South. Nature and extent, fate and transport of impacts from source areas to impacted and unimpacted areas, information needed to support remedial planning were considered during the vapor intrusion  pathway evaluation and is presented in Section 3.2.2 of this report. The vapor intrusion pathway is further evaluated as part of the human health and ecological risk assessment, the results of which are presented in  Appendix E and summarized as presented in Section 5 of this report. Vadose Zone Mass Flux to Groundwater Modeling Vadose zone mass flux to groundwater modeling and groundwater characterization was performed to identify potential sources of groundwater impacts (see Appendix C). The evaluation was performed in accordance  with Appendix D of the Comprehensive DQO Report: Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater  (MWH, 2013). The vadose zone mass flux to groundwater  approach includes evaluating the need for additional field data; evaluating the need to model vadose zone mass flux to groundwater; modeling; and determining if the vadose zone should be recommended for the CMS  or NFA. This evaluation is presented in Section 3.2.3 and Appendix C of this report. Air Dispersion Modeling Air dispersion modeling was performed for representative sources identified in Appendix B of the DQO Report: Recommended Approach for Air Dispersion Modeling, Boeing RCRA Facility Investigation Project, Santa  Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2013d). The approach for assessing air deposition impacts for other potential Boeing sources at SSFL, based on the results of the modeling of  representative sources is presented in Air Dispersion Evaluation Approach for Other Boeing Sources at Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2014b). No sources requiring air dispersion  modeling were identified at the EEL RFI site during this process. EN0317151003RDD PAGE 3 OF 5 TABLE 3‐1 Assessment Elements for Identification of Potential Contamination Sources and Weight‐of‐Evidence Documentation for CMS and NFA Recommendations for the EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Activities to Support NFA Area Recommendations for the  Assessment and documentation supporting recommendation that no release or potential release of any chemical previously used, stored, handled or disposed was identified within the EEL RFI site, other than the  CUAs identified in EEL RFI site media‐specific evaluations SMOUa Surface Water Drainage Documentation A comprehensive sitewide evaluation was performed by Boeing, DOE, and NASA to identify and document the locations of surface water drainage features and the direction of surface water flow at RFI sites and SSFL.  The results of this comprehensive evaluation were included in the GIS Gold Copy Data Management Tool submitted to DTSC in May 2012. No newly identified surface water drainages were observed at the EEL RFI site  through this process. Surface water drainage channels at the EEL RFI site have been investigated, the results of which were included in the 2008 EEL RFI Report. Portions of the drainage channels that were found to be  impacted are included in EEL CUA Cluster 1 and evaluated in media‐specific evaluations.  NPDES Surface Water Data Seeps and Springs Data Analytical Data Collected for Purposes Other than the RFI Historical surface water data collected under the NPDES program were evaluated. Surface water runoff at the SSFL is regularly monitored as part of the NPDES monitoring program under the oversight of the California  Regional Water Quality Control Board, Los Angeles Region. Two monitoring locations are monitored downgradient of the EEL RFI site: Outfall 002 at the south end of the Boeing RFI Subarea 10 and Outfall 018 at the  discharge of the R‐2 ponds in Administrative Area II. These discharge points are the ultimate discharge points for a large portion of the western half of SSFL. Ongoing monitoring and evaluation is being conducted under  the NPDES program.  Seeps and springs investigation and evaluation was conducted under the ongoing CFOU remedial investigation program. A summary of the evaluation of seeps and springs data is presented in Section 4.2  and Appendix  D of this report. Impacts to seeps or springs from the EEL RFI site releases are expected to be inconsequential based on the location of the EEL RFI site and magnitude of releases relative to the locations of seeps and  springs. Analytical data, field notes, and field logs from all prior field investigations were reviewed. Locations with chemical constituent concentrations above the required characterization levels are included in EEL CUA Cluster  1. These locations are evaluated further in media‐specific evaluations. Based on a review of field notes and records, no observations have been made during field activities that suggest a chemical release may have  occurred other than those documented in the 2008 EEL RFI Report, Addendum to Master RFI Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2013a), or Addendum to Master RFI Data Gap Work Plan ‐ Second Iteration, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California  (CH2M HILL, 2014a) for  the EEL RFI site. Notes:  Activities presented in this table are consistent with the activities presented in Figure 2 of the Comprehensive DQO Report (Chemical Use Area Confirmation and Conditional No Further Action Area Weight of Evidence Documentation for the Surficial Media Operable Unit; CH2M  HILL, 2013b). a Acronyms: AOC = area of concern CFOU = Chatsworth Formation Operable Unit CMS = corrective measures study CNFA = conditional no further action CUA = chemical use area DOE = United States Department of Energy DQO = data quality objectives DTSC = California Environmental Protection Agency, Department of Toxic Substances Control EEL = Environmental Effects Laboratory GIS = geographic information system NASA = National Aeronautics and Space Administration NPDES = National Pollutant Discharge Elimination System PCB = polychlorinated biphenyl RFA = RCRA facility assessment  RFI = RCRA facility investigation SMOU = Surficial Media Operable Unit SOP = standard operating procedure SSFL = Santa Susana Field Laboratory SWMU = Solid Waste Management Unit TPH = total petroleum hydrocarbons USEPA = United States Environmental Protection Agency Sources: Boeing. Pending. Comprehensive Submittal of Historical Boeing Documents. CH2M HILL. 2008. Group 5 – Central Portions of Areas III and IV RCRA Facility Investigation Report, Santa Susana Field Laboratory, Ventura County, California . November. CH2M HILL. 2013a. Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California . May. CH2M HILL. 2013b. Comprehensive Data Quality Objectives, RCRA Facility Investigation, Santa Susana Field Laboratory, Ventura County, California . March. CH2M HILL. 2013c. Recommended Approach for Assessing the Vapor Intrusion Pathway, Boeing RCRA Facility Investigation Project, Santa Susana Field Laboratory . (Appendix A to DQO Report). April. CH2M HILL. 2013d. Recommended Approach for Air Dispersion Modeling, Boeing RCRA Facility Investigation Project, Santa Susana Field Laboratory . (Appendix B to DQO Report). March. EN0317151003RDD PAGE 4 OF 5 TABLE 3‐1 Assessment Elements for Identification of Potential Contamination Sources and Weight‐of‐Evidence Documentation for CMS and NFA Recommendations for the EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Activities to Support NFA Area Recommendations for the  Assessment and documentation supporting recommendation that no release or potential release of any chemical previously used, stored, handled or disposed was identified within the EEL RFI site, other than the  CUAs identified in EEL RFI site media‐specific evaluations SMOUa CH2M HILL. 2014a. Addendum to Master RCRA Facility Investigation Data Gap Work Plan ‐ 2nd Iteration, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California . April. CH2M HILL. 2014b. Air Dispersion Evaluation Approach for Other Boeing Sources at Santa Susana Field Laboratory, Ventura County, California.  June 26. CH2M HILL. 2015a. Sanitary Sewer System Assessment for Boeing RFI Subareas, Santa Susana Field Laboratory, Ventura County, California . January. CH2M HILL. 2015b. Reclaimed Water System Assessment for Boeing RFI Subareas, Santa Susana Field Laboratory, Ventura County, California . January. CH2M HILL. 2015c. Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California . February 10. CH2M HILL and MWH. 2008a. Standard Operating Procedure, Building Feature Evaluation and Sampling, Santa Susana Field Laboratory, Ventura County, California. Prepared for The Boeing Company, The National Aeronautics and Space Administration, and The United States  CH2M HILL and MWH. 2008b. Standard Operating Procedure, Onsite Debris Survey and Sampling Methodology, Santa Susana Field Laboratory, Ventura County, California. Prepared for The Boeing Company, United States Department of Energy, National Aeronautics and Space  ICF. 1993. Current Conditions Report and Draft RCRA Facility Investigation Work Plan, Areas I and III, Santa Susana Field Laboratory, Ventura County, California. October. MWH Global (MWH). 2004. RCRA Facility Investigation Program Report, Surficial Media Operable Unit, Santa Susana Field Laboratory, Ventura County, California.  July. MWH Global. 2009. Sitewide Groundwater Remedial Investigation Report . MWH Global. 2012. Technical Memorandum. Natural Gas Pipeline GIS Feature Class, Santa Susana Field Laboratory, Ventura County, California.  April 6.  MWH Global. 2013. Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater, Santa Susana Field Laboratory . March.  Science Applications International Corporation. 1991. Final RCRA Facility Assessment Report for Rockwell International Corporation, Rocketdyne Division, Santa Susana Field Laboratory, Ventura County, California. Prepared for USEPA Region IX.  July. EN0317151003RDD PAGE 5 OF 5 TABLE 3‐2 Chemical Use Summary for EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use Area Types and Typical Target Analytical Suites  Chemical  Use Area  Chemical Use Area Name Numbera,h,i 1 EEL Cryogenic Test Cell (Building 3271) Potential Chemicals Used, Stored,  Handled, or Disposed Solvents, metals, oil, IPA,  formaldehyde, hydrazine Solvents, metals, oil, IPA,  formaldehyde Solvents, metals, oil, IPA,  formaldehyde Hydraulic oil PCBs, SVOCs VOCs, metals, oil, IPA TPH PCBs, SVOCs Solvents, metals, oil Hydraulic oil Hydraulic oil Hydraulic oil Solvents, metals, oil, PCBs, IPA,  gasoline, RP‐1, hydrazine, methanol 2 EEL Storage (Buildings 3109 and 3908) 3 EEL Mechanics Workshop (Buildings 3227, 3264) 5 6 7 8 9 10 11 12 13 14 Tanks Transformers Hazardous Materials Storage Pad TPH Soil Excavation Area Transformers EEL Cryogenic Test Cell (Building 3108) Tanks Tanks Tanks EEL Cryogenic Laboratory (Building 3268) 15 STL‐IV Reclaimed Water Sprayfield (Western Side of EEL) TPH, VOCs, SVOCs, metals, pH, PCBs,  energetics, formaldehyde,  perchlorate, dioxins, inorganics,  hexavalent chromium, pesticides,  herbicides, cyanide, IPA 16 STL‐IV Reclaimed Water Sprayfield (Eastern Side of EEL) TPH, VOCs, SVOCs, metals, pH, PCBs,  energetics, formaldehyde,  perchlorate, dioxins, inorganics,  hexavalent chromium, pesticides,  herbicides, cyanide, IPA d Energetic Constituents Transformers Energetics,  Metals Perchlorate PCBs Petroleum Fuels EEL CUA  Cluster 1 VOCs  X Gasoline‐ Diesel‐/ Motor‐ range  oil‐range  Petroleum  Petroleum  Fuels ‐ TPH,  Fuels ‐ TPH,  BTEX SVOCs X 1 X X X X X X Xe 1 X X X X X X Xe NA NA 1 1 1 1 1 1 1 1 VOCs, SVOCs  (Formaldehyde,  NDMA)b X SVOCs, TPH,  SVOCs, TPH,  PCBs,  PCBs,  Metals Metals, pH Metals X X Fluoride,  Chloride,  Nitrate,  Sulfate,  Bromide X X X X X X X X X X X X X X X X X X TPH, Metals,  VOCs, SVOCs,  PCBs, Dioxins,  Asbestosc Leach  Fieldd Other Xe X Xe X X X X X X X X 1 X X X X X X X X X Xe, f 1 X X X X X X X X X Xe, f 17 Tanks Hydraulic oil NA Notes:  a  CUA 4 is an office building (Building 3905, but also referenced as Building 3805 in some historical documents) that did not have any chemical uses. b  Potential hydrazine impacts are evaluated by analyzing for hydrazine breakdown products: formaldehyde and NDMA. c  Metal and Inorganics Hydrazine‐related  Oil‐related  Debris Areas/  Compounds Materials Waste Oils (exclusive of debris areas) Fill Solvents X X Xe, g X SVOCs and dioxins are sampled for if burned materials are observed or suspected. Asbestos are sampled for if potentially asbestos‐containing materials are observed.  The chemical groups associated with leach fields do not represent chemical groups used, stored, or released at the leach fields themselves. The chemical groups associated with the buildings that the leach fields serviced are considered in the review of leach field characterization for completeness. e  Isopropyl alcohol  Dioxins, hexavalent chromium, pesticides, herbicides, and cyanide g  Methanol h  The following Potential CUAs were not carried forward as CUAs: A portion of Potential CUA A ‐ the structure northwest of Building 3905 A portion of Potential CUA B ‐ a small stretch of pipeline that extended from the STP‐3 RFI site to the STL‐IV Reclaimed Water Sprayfield on the eastern portion of EEL RFI site i  This Data Summary and Findings Report only pertains to the portions of the EEL RFI site located within Administrative Area III (and Boeing RFI Subarea 5/9 South); the portions of the EEL RFI site that are located within Administrative Area IV are being characterized by the United States Department of Energy. CUAs 5 and  6 and portions of CUAs 1 and 7 that were identified in Group 5 – Central Portions of Areas III and IV RCRA Facility Investigation Report, Environmental Effects Laboratory RFI Site, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2008) are located in Administrative Area IV and are therefore not the  subject of this report. f EN0317151003RDD PAGE 1 OF 2 TABLE 3‐2 Chemical Use Summary for EEL RFI Site RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use Area Types and Typical Target Analytical Suites  Chemical  Use Area  Numbera,h,i Chemical Use Area Name Potential Chemicals Used, Stored,  Handled, or Disposed EEL CUA  Cluster Solvents Petroleum Fuels VOCs  Gasoline‐ Diesel‐/ Motor‐ range  oil‐range  Petroleum  Petroleum  Fuels ‐ TPH,  Fuels ‐ TPH,  BTEX SVOCs Metal and Inorganics Hydrazine‐related  Oil‐related  Debris Areas/  Compounds Materials Waste Oils (exclusive of debris areas) Fill VOCs, SVOCs  (Formaldehyde,  NDMA)b SVOCs, TPH,  SVOCs, TPH,  PCBs,  PCBs,  Metals Metals, pH Metals Fluoride,  Chloride,  Nitrate,  Sulfate,  Bromide TPH, Metals,  VOCs, SVOCs,  PCBs, Dioxins,  Asbestosc Energetic Constituents Transformers Energetics,  Metals Perchlorate PCBs Leach  Fieldd Other Acronyms: BTEX = benzene, toluene, ethylbenzene, and xylene COPC = chemical of potential concern CUA = chemical use area EEL = Environmental Effects Laboratory IPA = isopropanol NA = not applicable NDMA = nitrosodimethylamine PCB = polychlorinated biphenyl RFI = RCRA facility investigation SVOC = semivolatile organic compound TPH = total petroleum hydrocarbons VOC = volatile organic compound Sources: CH2M HILL. 2008. Group 5 – Central Portions of Areas III and IV RCRA Facility Investigation Report, Santa Susana Field Laboratory, Ventura County, Californi a. November. CH2M HILL. 2013. Addendum to Master RFI Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California.  May. EN0317151003RDD PAGE 2 OF 2 TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  1  CUAs 2, 3, 8  through 16,  and portions  of CUAs 1 and  7a  Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Sources, Operational History, and Physical  Characteristics  Yes. A summary of the CUA sources, operational  history, and physical characteristics is provided below.  CUA 1: EEL Cryogenic Test Cell (Building 3271):  Identified as part of SWMU 6.9 in the RFA. Used for  testing various materials, including carbon and stainless  steel, under high‐pressure hydrogen conditions from  1968 through 2008. One‐ton and 20‐ton metal cooling  towers where KP‐1 (a nonhazardous substance used to  prevent buildup of scale and fouling deposits) was used  were also located near or at Building 3271.  CUA 2: EEL Storage (Buildings 3109 and 3908): EEL  equipment and material storage. It also contained one  structure feature near Building 3908.  CUA 3: EEL Mechanics Workshop (Buildings 3227 and  3264): Mechanics workshop. It also contained one  undefined feature south of Building 3264.  CUA 7: Hazardous Materials Storage Pad: Hazardous  materials were stored in drums on a concrete pad east  of the cryogenic laboratory.  CUA 8: TPH Soil Excavation Area: A removal action was  conducted east of the cryogenic laboratory and south  of the hazardous materials storage pad as part of the  DTSC‐approved 1993 Accelerated Corrective Action  Work Plan (Appendix I of the Current Conditions  Report; ICF, 1993). The removal action was based on  TPH results at location D‐3‐02, and 2 to 3 cubic yards of  soil were removed and disposed of offsite.  CUA 9: Transformers: Located south of the hazardous  materials storage pad and at Building 3268.  CUA 10: EEL Cryogenic Test Cell (Building 3108):  Contained a test cell associated with Building 3271.  Used for testing various materials including carbon and  stainless steel under high‐pressure hydrogen conditions  from 1968 through 2008.  CUA 11: Tanks: Small ASTs primarily used to store  hydraulic oil for the vacuum pumps and several  hydrogen and helium gas tanks.  CUA 12: Tanks: Small ASTs primarily used to store  hydraulic oil for the vacuum pumps and several  hydrogen and helium gas tanks.  CUA 13: Tanks: Small ASTs primarily used to store  hydraulic oil for the vacuum pumps and several  hydrogen and helium gas tanks.  CUA 14: EEL Cryogenic Laboratory (Building 3268):  Identified as part of SWMU 6.9 in the RFA. Used for  testing various materials including carbon and stainless  EN0317151003RDD Potential  Chemicals Used/  Stored  Study Question #2: Are the nature and extent of chemical distributions  characterized to required characterization levels, or are data adequate to  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  Study Question #3: Are data adequate to  understand the fate and transport of chemicals,  or are data adequate to recommend the CUA  cluster or a portion of the CUA cluster for CMS?  VOCs (including  Yes. A summary of the nature and extent of VOCs in soil and soil vapor is below.  Yes. A summary of the fate and transport of  Formaldehyde)  Soil Vapor: Thirty‐eight soil vapor samples were collected at 26 locations from 4  chemicals in soil and soil vapor is summarized  below.  to 10 feet bgs between 1997 and 2014 and were analyzed for VOCs. Benzene,  Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  RFI recommendation: NFA or  CMS Assessment  Study Question #5: Are  existing data sufficient to  perform remedial planning?  Yes. Chemicals in soil, soil vapor,  and vadose zone exceed action  levels. CMS is recommended for  these media in portions of EEL  CC 1.   Yes. CMS areas are identified  for benzene and TCE in soil  vapor and arsenic,  benzo(a)pyrene, and dioxins  toluene, and TCE in soil vapor samples exceeded the SVCLs. Benzene and  Migration via Air Dispersion and Deposition:  and furans TEQ for mammals  toluene were detected above their SVCLs at one and three sample locations,  No sources have been identified as requiring air  in soil at EEL CC 1 to address  respectively, in two areas: the southern portion of the EEL RFI site operational  dispersion modeling at the EEL RFI site. Therefore,  Human health and ecological risk  risks to human and/or  area and the southeast portion of the EEL RFI site reporting area, near the  air dispersion modeling was not performed for the  assessments were performed for  boundary of the STP‐3 RFI site reporting area. The lateral extent of benzene and  EEL RFI site.  the EEL RFI site. The results of the  ecological receptors.  toluene is defined by samples with results below SVCLs or SCLs (where soil  human health risk assessment  In addition, CMS areas and  Migration of VOCs to Air:  vapor results were not available), and the vertical extent is defined by bedrock.  indicate that the excess lifetime  locations are recommended  Data are adequate to evaluate the VI pathway. The  cancer risk for hypothetical future  for TCE, perchlorate, 2,4‐ TCE was detected above its SVCL in the eastern and southern portions of the  nature and extent of VOCs in soil and soil vapor  dichlorophenoxybutyric acid,  EEL RFI site operational area and its highest concentration was detected  suburban residents exceeds 1 X  are presented under Study Question #2. As  southwest of the former hazardous materials storage pad (CUA 7). The lateral  10‐6, and the noncancer hazard  MCPA, beta‐benzene  presented in the Vapor Intrusion Assessment,  hexachlorocyclohexane,  extent of TCE is defined by samples with results below SVCLs and the vertical  index for hypothetical future  Boeing RFI Subarea 5/9 South, Santa Susana Field  suburban residents exceeds 1.  heptachlor, heptachlor  extent is defined by bedrock.   Laboratory, Ventura County, California  Benzene and TCE in soil vapor and  epoxide, and nitrate based on  Soil: Sixty‐nine soil samples were collected at 34 locations from 0 to 10.5 feet  (CH2M HILL, 2015a), soil vapor concentrations are  arsenic, benzo(a)pyrene, and  the results of the vadose  bgs between 1993 and 2014 and were analyzed for at least one VOC. VOCs were  below the VI characterization levels in many areas  2,3,7,8‐TCDD TEQ in soil were  zone to groundwater  not detected above their SCLs.   above the VOC groundwater plume outside of  evaluation.  identified as risk drivers for  Thirty‐one soil samples were collected at 14 locations from 0.5 to 10.5 feet bgs  CUAs. Therefore, the occurrence of VOCs in soil  hypothetical future suburban  Sufficient data are available  between 1998 and 2014 and were analyzed for formaldehyde. Formaldehyde  vapor at concentrations above VI characterization  residents. Additionally, arsenic,  to define the lateral and  was not detected above its reporting limit.  levels (which are based on default regulatory  benzo(a)pyrene, and 2,3,7,8‐TCDD  vertical extents of these  attenuation factors) at the EEL RFI site appears to  TEQ were identified as chemicals  SVOCs (including  Yes. A summary of the nature and extent of SVOCs in soil is below.   chemicals for the purposes of  be more strongly associated with residual VOCs in  for potential hot spots.  NDMA and  remedial planning. The  Soil: Eighty‐seven soil samples were collected at 40 locations from 0 to 10.5 feet  soil associated with releases from CUAs at EEL  Isopropanol)  recommended CMS areas  The results of the ecological risk  bgs between 2008 and 2014 and were analyzed for at least one SVOC.  rather than off‐gassing from groundwater. Risks  and locations are presented  assessment indicate that the  Benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,  associated with VI were evaluated as part of the  in Section 6. The size and  hazard quotient for ecological  benzo(k)fluoranthene, chrysene, and pyrene were detected above their SCLs in  human health risk assessment for the EEL RFI site,  one sample in the western sprayfield near the drainage channel. The lateral and  the results of which are summarized under Study  receptors exceeds 1. Dioxins and  shape of the CMS areas and  furans TEQ for mammals was  locations are based on  vertical extents of these SVOCs are defined by samples with results below SCLs.  Question #4.  identified as a risk driver for  professional judgement that  Sixty‐seven soil samples were collected at 32 locations from 0 to 10.5 feet bgs  Migration via Surface Water:  ecological receptors. Additionally,  includes an evaluation of  between 2008 and 2014 and were analyzed for NDMA. NDMA was not detected  factors such as media, site  dioxins and furans TEQ for  SVOCs, PCBs, dioxins and furans, pesticides,  above its reporting limit.  mammals was identified as a  features and topography,  herbicides, and metals (including hexavalent  Seven soil samples were collected at 3 locations from 0.5 to 6 feet bgs in 2013  chemical for potential hot spots.  data distribution, and  chromium) have been detected in surface soil  and were analyzed for isopropanol. Isopropanol was not detected above its  concentration magnitudes  samples from CUAs 1, 8, 11, 14, 15, and 16 at  CMS is also recommended for  reporting limit.  and gradients. A soil CMS  concentrations that exceed SCLs; however,  eight chemicals in the vadose  area in the western end of  downslope surface soil concentrations of these  TPH  Yes. A summary of the nature and extent of TPH in soil is below.   zone for the protection of  the EEL RFI site reporting  constituents are below SCLs (except for dioxins  groundwater based on the vadose  Soil: Sixty‐five soil samples were collected at 36 locations from 0 to 10.5 feet  and furans, which are described further below).  zone to groundwater evaluation.  area addresses chemical risk  bgs between 1993 and 2013 and were analyzed for TPH. Total recoverable  drivers detected in soil  Therefore, potential migration via surface water  TCE, perchlorate, 2,4‐DB, MCPA,  petroleum hydrocarbons were detected at sample location D‐3‐02 at a  samples collected from the  runoff is adequately characterized and surface  beta‐BHC, heptachlor, heptachlor  concentration of 11,000 mg/kg and a removal action was performed in this area  drainage channel. Other soil  water migration from the EEL RFI site is not  epoxide, and nitrate‐NO  are  3 (CUA 8) to remove TPH‐impacted soil.   CMS areas address chemical  indicated. As described in the response to Study  recommended for CMS in the  The next highest TPH concentration detected was oil‐range organics (C30‐C40)  Question #2, dioxins and furans have been  risk drivers detected in soil  vadose zone at EEL CC 1 because  south of Building 3271. Concentrations of TPH decrease with distance from this  detected in shallow soil at EEL and nearby RFI sites  samples not collected from  concentrations exceeded  location. SCLs have not been developed for TPH; potential risks associated with  above their SCLs, and their occurrence is not  drainage channels.   screening values in vadose zone  petroleum hydrocarbons are evaluated using BTEX and PAH data. BTEX and PAH  limited to past operational use areas.  samples at EEL CC 1 and transport  No further action is  data are located near each TPH sample location and the nature and extent of  Furthermore, dioxins and furans detected above  recommended for soil, soil  modeling estimated they would  chemical distributions are described above. BTEX and PAHs were not detected  PAGE 1 OF 7 TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  Sources, Operational History, and Physical  Characteristics  steel under high‐pressure hydrogen conditions from  1968 through 2008. Contained multiple transformers,  one of which showed staining around the valve. There  were 1‐ton and 30‐ton metal cooling towers near  Building 3268 that used KP‐1 (a nonhazardous  substance used to prevent buildup of scale and fouling  deposits). Documented historical releases of 2.5 to 80  gallons of water paint, aluminum powder and water,  coolant, and hydraulic fluid occurred between 1975  and 1996.  CUA 15 (previously portion of Potential CUA A):  Western STL‐IV Reclaimed Water Sprayfield: A  sprayfield located in western portion of the EEL RFI site  reporting area that received reclaimed water from the  STL‐IV RFI site.  Potential  Chemicals Used/  Stored  PCBs  Dioxins and  Furans  CUA 16 (previously portion of Potential CUA B):  Eastern STL‐IV Reclaimed Water Sprayfield: A sprayfield  located in eastern portion of the EEL RFI site reporting  area that received reclaimed water from the STL‐IV RFI  site.   The site is located on the border between  Administrative Areas III and IV. Structures at the site  have been demolished, and tanks have been removed.  The site is currently unpaved due to demolition  activities performed in 2012. Historically, areas near  the buildings were paved. Topography in the central  portion of the site slopes to the south and east.  Topography in the western portion of the EEL RFI site  reporting area slopes to the south and west.  Throughout most of the site, soil is generally thin,  typically ranging from less than 3 feet to 10 feet thick.  Soil in the undisturbed areas of the site consists of  weathered Chatsworth Formation materials, which are  primarily fine‐grained, silty sands and clayey silts.  Surface water exists intermittently in ephemeral  drainages at the western end of the EEL RFI site  reporting area as the result of seasonal precipitation  events. Surface water in the ephemeral drainages flows  south through the Compound A RFI site and ultimately  to the R‐2 Discharge Ponds in Administrative Area II.  Surface water runoff in the other parts of the EEL RFI  site reporting area flows via sheet flow generally south  to the pond at the STP‐3 RFI site.    Pesticides and  Herbicides  Study Question #3: Are data adequate to  Study Question #2: Are the nature and extent of chemical distributions  understand the fate and transport of chemicals,  characterized to required characterization levels, or are data adequate to  or are data adequate to recommend the CUA  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  cluster or a portion of the CUA cluster for CMS?  above their SCLs in samples located near the two locations with the highest TPH  the SCL in samples collected within the drainage  concentrations.  channel at the western end of the EEL RFI site  reporting area have likely migrated from  Yes. A summary of the nature and extent of PCBs in soil is below.   upgradient locations. Although dioxins and furans  Soil: Forty‐seven soil samples were collected at 22 locations from 0 to 10.5 feet  are not defined to below SCLs within the footprints  bgs between 2003 and 2014 and were analyzed for PCBs. Either Aroclor‐1254 or  of the EEL RFI site reporting area, dioxins and  Aroclor‐1260 were detected above SCLs in nine samples. The nine samples with  furans are generally defined to below the SCL on a  exceedances are within the drainage channel at the west end of the EEL RFI site  regional scale. No other chemicals were detected  reporting area, within the western sprayfield, southwest of Building 3268, or  above SCLs in surface soil samples at the EEL CC 1.  south of Building 3905. The lateral and vertical extents of PCBs are defined by  Migration to Vadose Bedrock and Mass Flux to  samples with results below SCLs or by bedrock.   Groundwater:   Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  RFI recommendation: NFA or  CMS Assessment  impact groundwater at  concentrations above screening  levels during the 100‐year model  simulation.  Study Question #5: Are  existing data sufficient to  perform remedial planning?  vapor, and vadose zone  bedrock in the portions of the  EEL RFI site reporting area  outside the recommended  CMS areas and locations.  Data are adequate to evaluate the migration of  chemicals to vadose zone bedrock and  Soil: Fifty‐two soil samples were collected at 25 locations from 0 to 10.5 feet bgs  groundwater. VOCs, SVOCs, PAHs, perchlorate,  between 2008 and 2014 and were analyzed for dioxins and furans. Dioxins and  TPHs, PCBs, herbicides, pesticides, dioxins and  furans were detected above the SCL in 24 samples. The exceedances of dioxins  furans, metals, and inorganics were detected in  and furans above the SCL occur mostly in surface soil and is found both within  the vadose zone (soil or soil vapor) above vadose  operational and non‐operational areas of the EEL RFI site reporting area. Dioxins  zone screening values and were evaluated for  and furans have also been detected above the SCL in shallow soil at nearby RFI  potential threat to groundwater as described in  sites, and occurrence is not limited to past operational areas. Furthermore,  Appendix C. The following eight chemicals were  dioxins and furans detected above the SCL in samples collected within the  identified as posing a potential threat to  drainage channel at the western end of the EEL RFI site reporting area have  groundwater at EEL CC 1 based on evaluations  likely migrated from upgradient locations. Although dioxins and furans are not  presented in Appendix C: TCE, perchlorate, 2,4‐ defined to below SCLs within the footprints of the EEL RFI site reporting area,  dichlorophenoxybutyric acid, MCPA, beta‐benzene  dioxins and furans are generally defined to below the SCL on a regional scale.  hexachlorocyclohexane, heptachlor, hepthachlor  epoxide, and nitrate. All other chemicals were  Yes. A summary of the nature and extent of pesticides and herbicides in soil is  detected at concentrations that are protective of  below.   groundwater.   Soil: Twenty‐nine soil samples were collected at 13 locations from 0 to 10 feet  bgs between 2013 and 2014 and were analyzed for pesticides. 4,4’‐DDT was  detected above its SCL in two samples within the drainage channel at the  western end of the EEL RFI site reporting area and south of Building 3905. The  lateral and vertical extent of 4,4’‐DDT is defined by samples with results below  SCLs.   Yes. A summary of the nature and extent of dioxins and furans in soil is below.   Twenty‐two soil samples were collected at nine locations from 0 to 10 feet bgs  in 2013 and were analyzed for herbicides. MCPA was detected above its SCL in  one sample, located within the drainage channel at the western end of the EEL  RFI site reporting area. The lateral and vertical extents of MCPA is defined by  samples with results below SCLs.   Energetics and  Perchlorate  Yes. A summary of the nature and extent of energetics and perchlorate in soil is  below.   Soil: Thirty‐five soil samples were collected at 15 locations from 0.5 to 10.5 feet  bgs between 2008 and 2014 and were analyzed for at least one energetic.  Twenty‐three soil samples were collected at 11 locations between 0.5 to 10.5  feet bgs between 2008 and 2013 and were analyzed for perchlorate. Energetics  and perchlorate were not detected above their SCLs.  Metals (including  Yes. A summary of the nature and extent of metals in soil is below.   Hexavalent  Soil: One‐hundred and fifty‐five soil samples were collected at 73 locations from  Chromium)  0 to 15.5 feet bgs between 1993 and 2014 and were analyzed for at least one  metal. Arsenic is the metal most frequently detected at concentrations  PAGE 2 OF 7 EN0317151003RDD TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Sources, Operational History, and Physical  Characteristics  Potential  Chemicals Used/  Stored  Study Question #2: Are the nature and extent of chemical distributions  characterized to required characterization levels, or are data adequate to  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  significantly higher than its SCL. Arsenic was detected in 108 of the 112 samples  for which it was analyzed. Arsenic was detected above the SCL in nine samples.  The nine samples with exceedances are within the historical TPH soil excavation  area (CUA 8), southeast of the transformer area (CUA 9), just east of the EEL RFI  site operational area (CUA 16), southwest of Building 3109 (CUA 2), at the south  end of Building 3271 (CUA 1), and north and south of Building 3264 (CUA 3). The  lateral and vertical extents of arsenic are defined by samples with results below  SCLs or by bedrock.   Study Question #3: Are data adequate to  understand the fate and transport of chemicals,  or are data adequate to recommend the CUA  cluster or a portion of the CUA cluster for CMS?  Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  Study Question #5: Are  existing data sufficient to  perform remedial planning?  RFI recommendation: NFA or  CMS Assessment  Thirty‐seven soil samples were collected at 20 locations from 0 to 10.5 feet bgs  between 1998 and 2014 and were analyzed for hexavalent chromium.  Hexavalent chromium was detected above the SCL in four samples. The four  samples with exceedances are located within and along the bank of the  drainage channel at the western end of the EEL RFI site reporting area and at  the eastern end of the EEL RFI site operational area. The lateral and vertical  extents of hexavalent chromium are defined by samples with results below SCLs  or by bedrock.  Inorganics  (including  Cyanide)  Radionuclides  Yes. A summary of the nature and extent of inorganics in soil is below.   Soil: Seventy‐four soil samples were collected at 42 locations from 0 to 10.5 feet  bgs between 1993 and 2014 and were analyzed for at least one inorganic. Forty‐ four soil samples were collected at 9 locations from 0 to 10 feet bgs in 2013 and  were analyzed for cyanide. Inorganics and cyanide were not detected above  their SCLs.  Yes. A summary of the nature and extent of radionuclides in soil is below.   Soil: Five soil samples were collected at five locations from 0 to 0.5 foot bgs  between 2010 and 2011 and were analyzed for radionuclides to assess  migration from upgradient Area IV sources where radiological materials were  used. Strontium‐90 was detected above the SCL in one sample within the  drainage channel at the western end of the EEL RFI site reporting area. The  upstream and downstream extent of strontium‐90 is defined by samples with  results below SCLs. No other radionuclides were detected at concentrations  exceeding SCLs.  1  Potential CUA  Yes. Potential CUA A was identified in the May 2013  A  Addendum to the Master RFI Data Gap Work Plan for  the EEL RFI site (CH2M HILL, 2013) to evaluate the  western sprayfield and one structure northwest of  Building 3905. Although the spray field is being  evaluated as CUA 15, the structure northwest of  Building 3905 is not being evaluated further as a CUA.  However, the entire footprint of former Potential CUA  A is located within EEL CC 1.  VOCs, SVOCs,  TPH, PCBs, and  Metals   Yes. A summary of the nature and extent of VOCs in soil vapor and SVOCs, TPH,  PCBs, and metals in soil at the structure northwest of Building 3905 is below.   Soil Vapor: Two soil vapor samples were collected at one location from 5 to 9.8  feet bgs in 2013 and were analyzed for VOCs. VOCs were not detected in soil  vapor above their SVCLs.  Yes. A summary of the chemicals  Yes. A summary of the fate and transport of  chemicals in soil and soil vapor is presented above  exceeding action levels and the  for EEL CC 1.   RFI recommendations are  presented above for EEL CC 1.    Yes. An assessment of the  existing data to perform  remedial planning is  presented above for EEL CC 1.   Soil: Three soil samples were collected at one location from 0 to 6 feet bgs in  2013 and were analyzed for at least one of the following chemical groups:  SVOCs, TPH, PCBs, and metals. These chemicals were not detected above their  SCLs.  The portion of Potential CUA A that does not fall within the footprint of the  sprayfield was not retained in CUA 15 (or any other CUA) because chemicals  were not detected above their SCLs and SVCLs in samples collected near the  structure northwest of Building 3905.  1   Potential CUA  Yes. Potential CUA B was identified in the May 2013  B  Addendum to the Master RFI Data Gap Work Plan for  the EEL RFI site (CH2M HILL, 2013) to evaluate the  eastern sprayfield. Although the sprayfield is being  EN0317151003RDD VOCs, SVOCs,  TPH, PCBs,  Dioxins and  Furans,  Yes. A summary of the nature and extent of VOCs in soil vapor and VOCs,  Yes. A summary of the fate and transport of  SVOCs, TPH, PCBs, dioxins and furans, pesticides, herbicides, energetics,  chemicals in soil and soil vapor is presented above  perchlorate, metals, inorganics, hexavalent chromium, and cyanide in soil along  for EEL CC 1.   the pipeline is below.   Yes. A summary of the chemicals  exceeding action levels and the  RFI recommendations are  presented above for EEL CC 1.  Yes. An assessment of the  existing data to perform  PAGE 3 OF 7 TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Sources, Operational History, and Physical  Characteristics  evaluated as CUA 16, a small stretch of pipeline that  extended from the STP‐3 RFI site to the STL‐IV  Reclaimed Water Sprayfield on the eastern portion of  EEL RFI site reporting area that was also part of  Potential CUA B is not being evaluated further as a  CUA. However, the entire footprint of former Potential  CUA B is located within EEL CC 1.  Potential  Chemicals Used/  Stored  Pesticides,  Herbicides,  Energetics,  Perchlorate,  Metals,  Inorganics,  Hexavalent  Chromium, and  Cyanide  Study Question #3: Are data adequate to  understand the fate and transport of chemicals,  or are data adequate to recommend the CUA  cluster or a portion of the CUA cluster for CMS?  Study Question #2: Are the nature and extent of chemical distributions  characterized to required characterization levels, or are data adequate to  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  Soil Vapor: One soil vapor sample was collected at one location from 5 to 5.5  feet bgs in 2013 and was analyzed for VOCs. VOCs were not detected in soil  vapor above their SVCLs.  Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  Study Question #5: Are  existing data sufficient to  perform remedial planning?  RFI recommendation: NFA or  CMS Assessment    remedial planning is  presented above for EEL CC 1.   Soil: Five soil samples were collected at one location from 0 to 10 feet bgs in  2013 and were analyzed for at least one of the following chemical groups: VOCs,  SVOCs, TPH, PCBs, dioxins and furans, pesticides, herbicides, energetics,  perchlorate, metals, inorganics, hexavalent chromium, and cyanide. Only dioxins  and furans were detected above its SCL. The other chemicals were not detected  above their SCLs. Dioxins and furans have also been detected above their SCLs  in shallow soil at nearby RFI sites and do not appear to be related to Potential  CUA B.  The small stretch of reclaimed water system pipeline that extended from the  STP‐3 RFI site to the STL‐IV Reclaimed Water Sprayfield on the eastern portion  of EEL RFI site reporting area that was originally identified as part of Potential  CUA B was not retained in CUA 16 (or any other CUA) because, other than  dioxins and furans, chemicals were not detected at concentrations above their  SCLs and SVCLs in samples collected along the pipeline. Dioxins and furans were  found throughout the EEL RFI site reporting area, including areas not associated  with the reclaimed water system, and at nearby RFI sites. The occurrence of  dioxins and furans in the samples may be attributable to other sources and are  generally defined to below the SCL on a regional scale. Therefore, the portion of  Potential CUA B that included the small stretch of reclaimed water system  pipeline was not retained as a CUA.  Reclaimed Water System  Yes. Two sprayfields (CUAs 15 and 16) and  approximately 550 feet of reclaimed water pipeline are  located within the EEL RFI site reporting area.  Reclaimed water was transported from the STL‐IV RFI  site via pipelines through the Compound A and STP‐3  RFI sites and discharged to the ground at two  sprayfields at the western and eastern ends of the EEL  RFI site reporting area. Additionally, four surface water  drainages converge into one primary drainage along  the western end of the EEL RFI site reporting area  before continuing south to the Compound A RFI site.  VOCs, SVOCs,  TPH, PCBs,  Dioxins and  Furans,  Pesticides,  Herbicides,  Energetics,  Perchlorate,  Metals,  Inorganics,  Hexavalent  Chromium, and  Cyanide  Yes. Samples within the sprayfields and near pipelines and drainages were used  to evaluate the nature and extent of chemical distributions relative to the  reclaimed water system within the EEL RFI site reporting area. A summary of the  nature and extent of VOCs in soil vapor and VOCs, SVOCs, TPH, PCBs, dioxins  and furans, pesticides, herbicides, energetics, perchlorate, metals, inorganics,  hexavalent chromium, and cyanide in soil is below.   Yes. A summary of the chemicals  Yes. A summary of the fate and transport of  chemicals in soil and soil vapor is presented above  exceeding action levels and the  RFI recommendations are  for EEL CC1.   presented above for EEL CC1.    Yes. An assessment of the  existing data to perform  remedial planning is  presented above for EEL CC1.    Soil Vapor: Sixteen soil vapor samples were collected at 12 locations from 4 to  10 feet bgs between 1997 and 2013 near the reclaimed water system and were  analyzed for VOCs. Benzene, toluene, and TCE were detected above their SVCLs  in two locations; however, these chemicals may be attributed to other sources  at the EEL RFI site due to their occurrence elsewhere at the EEL RFI site.  Soil: Ninety‐five soil samples were collected at 40 locations from 0 to 10 feet  bgs between 1993 and 2014 near the reclaimed water system and were  analyzed for at least one of the following chemical groups: VOCs, SVOCs, PCBs,  dioxins and furans, pesticides, herbicides, energetics, perchlorate, metals,  inorganics, hexavalent chromium, and cyanide. SVOCs, PCBs, dioxins and furans,  pesticides, and metals (including hexavalent chromium) were detected above  their SCLs.   SVOCs were detected above their SCLs in one sample in the western sprayfield  near the drainage channel. Other detections of similar SVOCs were also  detected in the portion of the sprayfield in Administrative Area IV. The SVOCs  may be associated with the historic use of the sprayfield, or they may be  associated with historic operations in this area since the extent of SVOC  exceedances is not confined to the sprayfield boundaries. The nature and extent  of the SVOCs exceeding SCLs in the western sprayfield are defined by bedrock or  samples with results below SCLs.   PAGE 4 OF 7 EN0317151003RDD TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Sources, Operational History, and Physical  Characteristics  Potential  Chemicals Used/  Stored  Study Question #2: Are the nature and extent of chemical distributions  characterized to required characterization levels, or are data adequate to  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  Study Question #3: Are data adequate to  understand the fate and transport of chemicals,  or are data adequate to recommend the CUA  cluster or a portion of the CUA cluster for CMS?  Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  Study Question #5: Are  existing data sufficient to  perform remedial planning?  RFI recommendation: NFA or  CMS Assessment  PCBs were detected above their SCLs within the footprints of the sprayfields and  downstream drainage channels. However, PCBs were also detected above their  SCLs in operational areas not associated with the reclaimed water system.  Based on the distribution of PCBs throughout the EEL RFI site reporting area,  PCBs in soil do not appear to be associated with potential releases from the  reclaimed water system.  Various metals (cadmium, antimony, barium, silver, and arsenic) were detected  above their SCLs within the footprints of the sprayfields and downstream  drainage channels. Various metals, including some of those listed above, were  detected throughout the EEL RFI site reporting area and in areas not associated  with the reclaimed water system. Based on the distribution of metals  throughout the EEL RFI site reporting area, the elevated metals concentrations  within the EEL RFI site reporting area do not appear to be associated with  potential releases from the reclaimed water system. The extent of metal  concentrations exceeding SCLs are defined by bedrock or samples with  concentrations below SCLs.   Hexavalent chromium was detected at two locations in the eastern sprayfield  and at one location in the drainage channel at the western sprayfield at  concentrations above the SCL. However, the hexavalent chromium detections  are slightly above the USL95 background threshold value, and hexavalent  chromium has been detected at concentrations below the SCL in other samples  collected within the sprayfields. Therefore, hexavalent chromium detections at  the sprayfields at the EEL RFI site do not appear to be associated with potential  releases from the reclaimed water system. Hexavalent chromium  concentrations exceeding the SCL are defined by bedrock or by samples with  concentrations below SCLs.   A pesticide (4,4‐DDT) was detected at one location slightly above its SCL in the  western sprayfield. This pesticide exceedance may be associated with potential  releases from the sprayfield. The 4,4‐DDT detection exceeding the SCL is defined  by bedrock or samples with concentrations below SCLs.   Sodium was detected at one location above its SCL in the eastern sprayfield.  However, sodium was not detected above its SCL in any other samples in the  sprayfield and the concentration of sodium did not exceed the USL95  background threshold value and is considered consistent with background  concentrations. Therefore, sodium does not appear to be associated with  potential releases from the reclaimed water system. The sodium exceedance is  defined by bedrock or samples with concentrations below SCLs.   Dioxins and furans were detected above their SCLs within the sprayfields,  adjacent to pipelines, and in drainage channels. However, dioxins and furans  were detected throughout the EEL RFI site reporting area and do not appear to  be related to releases from the reclaimed water system.   Sanitary Sewer System  EN0317151003RDD Yes. As presented in the Sanitary Sewer Assessment  Technical Memorandum (CH2M HILL, 2015b), there are  approximately 750 feet of sanitary sewer pipeline and  two sanitary sewer manholes within the EEL RFI site  reporting area. Sanitary sewer pipeline segments 5/9‐3,  5/9‐4, 5/9‐12, 5/9‐15, and portions of 5/9‐2, 5/9‐5, 5/9‐ 6, and 5/9‐14 are located within the EEL RFI site  reporting area. Sanitary sewage was conveyed from the  VOCs, SVOCs,  Formaldehyde,  TPH, PCBs,  Dioxins and  Furans,  Energetics,  Perchlorate,  Metals,  Yes. Data near (within approximately 15 feet from) the sanitary sewer pipelines,  manholes, and building exits were used to evaluate the nature and extent of  chemical distributions. A summary of the nature and extent of VOCs in soil  vapor and VOCs, SVOCs, formaldehyde, TPH, PCBs, dioxins and furans,  energetics, perchlorate, metals, inorganics, alcohol, pesticides, and hexavalent  chromium in soil is below.   Yes. A summary of the chemicals  Yes. A summary of the fate and transport of  chemicals in soil and soil vapor is presented above  exceeding action levels and the  for EEL CC 1.   RFI recommendations are  presented above for EEL CC 1.    Yes. An assessment of the  existing data to perform  remedial planning is  presented above for EEL CC 1.   PAGE 5 OF 7 TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Sources, Operational History, and Physical  Characteristics  west (from the STL‐IV RFI site), east (from the  Compound A RFI site), and from Buildings 3268 and  3905 at the EEL RFI site south to the sewage treatment  plant at the STP‐3 RFI site. Known depths for sewer  segments in the EEL RFI site range from approximately  5 to 10 feet bgs.   Potential  Chemicals Used/  Stored  Inorganics,  Alcohol,  Pesticides,  Hexavalent  Chromium,  Terphenyls, and  Radionuclides  Study Question #2: Are the nature and extent of chemical distributions  characterized to required characterization levels, or are data adequate to  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  Study Question #3: Are data adequate to  understand the fate and transport of chemicals,  or are data adequate to recommend the CUA  cluster or a portion of the CUA cluster for CMS?  Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  RFI recommendation: NFA or  CMS Assessment  Study Question #5: Are  existing data sufficient to  perform remedial planning?  Soil Vapor: Sixteen soil vapor samples were collected at 11 locations from 4 to  10 feet bgs between 1997 and 2013 and were analyzed for VOCs. VOCs were  not detected in soil vapor at concentrations above their SVCLs.  Soil: Twenty‐five soil samples were collected at 17 locations from 5 to 15.5 feet  bgs between 2008 and 2014 near the sanitary sewer system and were analyzed  for at least one of the following chemical groups: VOCs, SVOCs, formaldehyde,  TPH, PCBs, dioxins and furans, energetics, perchlorate, metals, inorganics,  alcohol, pesticides, and hexavalent chromium. Dioxins and furans and metals  (including hexavalent chromium) were detected above their SCLs.   Dioxins and furans and metals were detected above their SCLs in samples  located near the sanitary sewer pipelines. However, dioxins and furans and  metals (other than hexavalent chromium) were found throughout the EEL RFI  site reporting area, including areas not associated with the sanitary sewer  system, and generally at higher concentrations in shallow soil. Based on the  distribution of dioxins and furans and metals throughout the EEL RFI site  reporting area and their low mobility in the environment, there are no  indications that dioxins and furans and metals in soil within the EEL RFI site  reporting area are associated with potential releases from the sanitary sewer  system. Based on the locations and depths of samples with hexavalent  chromium concentrations above its SCL, hexavalent chromium exceedances  within the EEL RFI site reporting area do not appear to be associated with  potential releases from the sanitary sewer system. The hexavalent chromium  detections exceeding the SCL are defined in vertical and horizontal extents by  bedrock or samples with results below SCLs.   Terphenyls and radionuclides, which are potentially associated with the sanitary  sewer system, were evaluated on a subarea scale rather than on an individual  RFI site scale. Terphenyls were used in small quantities and do not appear to  have migrated from Administrative Area IV to Boeing RFI Subarea 5/9 South via  the sanitary sewer system and were not investigated in the EEL RFI site.  Although there are detections of radionuclides above their SCLs within building  footprints and near sanitary sewer system building exit points in Boeing RFI  Subarea 5/9 South, radionuclides were not detected above their SCLs at points  downstream along the pipeline. Based on the isolated detections of  radionuclides above their SCLs and their limited extent within the sanitary  sewer system, radionuclides do not appear to have impacted the sanitary sewer  system and were consequently not investigated along the sanitary sewer system  in the EEL RFI site reporting area.  The nature and extent of these chemical groups are also presented above in the  responses to Study Question #2 for each chemical group at EEL CC 1.  Notes:  a This Data Summary and Findings Report only pertains to the portions of the EEL RFI site located within Administrative Area III (and Boeing RFI Subarea 5/9 South); the portions of the EEL RFI site that are located within Administrative Area IV are being characterized by DOE. CUAs 5, 6, and 17 and portions of  CUAs 1 and 7 that were identified in Group 5 – Central Portions of Areas III and IV RCRA Facility Investigation Report, Environmental Effects Laboratory RFI Site, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2008) are located in Administrative Area IV and are therefore not the subject  of this report. CUA 4 is an office building (Building 3905, but also referenced as Building 3805 in some historical documents) that was identified in the 2008 Group 5 RFI Report. It did not have any chemical uses and was not carried forward in this report.  b Refer to the data tables and figures presented in Appendix A and Tables 4‐2 and 4‐3 for the analytical data associated with all samples listed in this table.  c Primary, duplicate, and split samples are counted for purposes of calculating the number of samples, number of detections, or number of detections exceeding characterization levels in this table. Excavated samples are not counted for purposes of calculating the number of samples, number of detections,  or number of detections exceeding characterization levels in this table. Analytical results for excavated, primary, duplicate, and split samples exceeding characterization levels are shown in Tables 4‐2 and 4‐3 for detect and nondetect results, respectively.  d This table summarizes and evaluates data collected within the EEL RFI site reporting area boundary.    PAGE 6 OF 7 EN0317151003RDD TABLE 4‐1  DQO Evaluation Findings for EEL RFI Site – Soil, Soil Vapor, and Vadose Zone Bedrock  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Use  Area or  EEL CUA  Potential CUA  Cluster   Number  Study Question #1: Are all potential sources and chemicals identified in  soil and sediment within CUAs and Potential CUAs?  Sources, Operational History, and Physical  Characteristics  Potential  Chemicals Used/  Stored  Study Question #2: Are the nature and extent of chemical distributions  characterized to required characterization levels, or are data adequate to  recommend the CUA cluster or a portion of the CUA cluster for CMS? b, c, d  Study Question #3: Are data adequate to  understand the fate and transport of chemicals,  or are data adequate to recommend the CUA  cluster or a portion of the CUA cluster for CMS?  Study Question #4: Do  concentrations of chemicals  within CUA Cluster exceed action  levels?  RFI recommendation: NFA or  CMS Assessment  Study Question #5: Are  existing data sufficient to  perform remedial planning?  Acronyms:  AST = aboveground storage tank  bgs = below ground surface  BTEX = benzene, toluene, ethylbenzene, and xylenes  CC = CUA cluster  CMS = corrective measures study  CUA = chemical use area  EEL = Environmental Effects Laboratory  MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  NDMA = nitrosodimethylamine  PAH = polycyclic aromatic hydrocarbon  PCB = polychlorinated biphenyl  RCRA = Resource, Conservation, and Recovery Act  RFA = RCRA Facility Assessment  RFI = RCRA Facility Investigation  SCL = soil characterization level  STP‐3 = Area III Sewage Treatment Plant  STL‐IV = Systems Test Laboratory IV  SVCL = soil vapor characterization level  SVOC = semivolatile organic compound  SWMU = solid waste management unit  TCE = trichloroethene  TEQ = toxicity equivalent  TPH = total petroleum hydrocarbons  VI = vapor intrusion  VOC = volatile organic compound  Sources:  CH2M HILL. 2013. Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California. May.  CH2M HILL. 2015a. Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California. February.   CH2M HILL. 2015b. Sanitary Sewer System Assessment for Boeing RFI Subareas, Santa Susana Field Laboratory, Ventura County, California. January.  ICF. 1993. Current Conditions Report and Draft RCRA Facility Investigation Work Plan, Areas I and III, Santa Susana Field Laboratory, Ventura County, California. October.    EN0317151003RDD PAGE 7 OF 7 Table 4-2 Data Summary for Detected Results for EEL RFI Site is provided on the attached CD     Table 4‐3 Data Summary for Nondetected Results for EEL RFI Site is provided on the attached CD    TABLE 4‐4 DQO Evaluation Findings for EEL RFI Site ‐ Groundwater and Seeps RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analytical  Group Study Question #3: Are data adequate to understand the fate and transport of  Study Question #4: Do concentrations of chemicals in groundwater  Study Question #2: Are the nature and extent of chemicals characterized to required  chemicals in groundwater, including volatilization of chemicals from  exceed action levels and/or do concentrations of chemicals present  RFI recommendation: NFA  characterization levels  in groundwater, or are data adequate to recommend the CUA cluster  groundwater to the vadose zone and migrations of chemicals to seeps and off‐ significant risk to current or future receptors (indoor air, seeps, or off‐ or CMS Assessment or portions of the CUA cluster for CMS? site wells, or are data adequate to recommend the CUA cluster or portions of  site wells)? the CUA cluster for CMS? Yes Yes Yes CMS Historical and recent VOC groundwater data are available for wells ES‐23, ES‐26, ES‐28, ES‐29,  ES‐30. Although these wells are associated with other RFI sites in Boeing RFI Subarea 5/9  South, they intercept the truncated particle tracks (that is, flow paths) from the EEL RFI site  and were used to characterize the nature and extent of VOCs in groundwater. Groundwater  samples collected at nearby well ES‐29 and downgradient wells ES‐26 and PZ‐051 were  analyzed for VOCs in one or more of the events during 2012‐2014. The most recent VOC  groundwater data available at wells within the EEL RFI site is from samples collected at wells  RS‐15 and RS‐17  in 2011, and RS‐37 in 2014.  VOCs The VOC groundwater plume sourced from the EEL RFI site is not expanding  Concentrations of cis‐1,2‐DCE and TCE are above GCLs in groundwater.  based on analysis of existing data from ES‐29, ES‐30, and RS‐15 and RS‐17, which  TCE was also detected at concentrations exceeding soil vapor  show stable, decreasing, or indeterminate concentration trends. VOC  characterization levels in soil vapor at the EEL RFI site. concentrations in downgradient wells are defined to below characterization  levels at locations expected to be far down the flow path, including the SP‐882  The vadose zone transport modeling groundwater protection evaluation  cluster, and there is a statistically significant downward (or stable/indeterminate)  for TCE indicates concentrations in vadose zone samples collected at the  trend in concentrations at existing wells.  EEL RFI site are in exceedance of vadose zone concentrations protective  of groundwater.  Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  Of the available recent data described above, VOCs were below GCLs in groundwater with  consequence in light of its distant location from, and magnitude of releases,  exception of cis‐1,2‐DCE and TCE.  Samples from wells RS‐15 and ES‐26 showed concentrations  relative to the location of these features.  For a seeps discussion in Boeing RFI  of both cis‐1,2‐DCE and TCE above GCLs where ES‐29 and ES‐30 only had TCE concentrations  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. above GCLs. Impacts at ES‐26 are interpreted to be related to the nearby STL‐IV RFI site and  are not included in the estimated footprint for impacted groundwater from the EEL RFI site. As part of the fate and transport evaluation, groundwater was evaluated as a    potential source of VOCs to indoor air through the vapor intrusion pathway for  The lateral extent of VOCs in groundwater at the EEL RFI site is currently defined by RS‐17 and  Subarea 5/9 South (CH2M HILL, 2014).  RS‐37 to the southwest, PZ‐028 to the east/northeast, PZ‐051 to the northeast, and wells in  southwest drainage to the south (that is, SP‐882 & RD‐06). Although there are no vertically  discrete sampling locations within EEL, sampling results from the vertical clusters to the west  and southwest near STL‐IV (RD‐55 and RD‐58 clusters) and to the south of the Burro Flats fault  (SP‐882G) show that VOCs have been characterized to below or near GCLs. Three‐dimensional  plume evaluations have been developed for groundwater impacts in Boeing RFI Subarea 5/9  South; descriptions and results are presented in Appendix B of the 5/9S DSFR. TCE and cis‐1,2‐DCE are  recommended for CMS  assessment in  groundwater. TCE is also recommended  for CMS in the vadose  zone for protection of  groundwater. For a data summary of individual VOCs results in groundwater (that is, number of locations  sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in Appendix D. SVOCs Yes Yes Recent SVOC data for the groundwater in and downgradient of the EEL RFI site are available.  Samples collected at EEL wells PZ‐050 and RS‐37 were analyzed for SVOCs in 2014 and samples  collected at downgradient wells ES‐29 and ES‐30  were analyzed for SVOCs during one or more  of the following years: 2011, 2012, 2013 and 2014. At these locations, no SVOCs were  detected at or above their GCLs.  SVOCs have not been detected historically or recently in groundwater at the EEL  SVOCs have not been detected historically or recently at or above GCLs in  RFI site.  groundwater at the EEL RFI site. No Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  consequence in light of its distant location from, and magnitude of releases,  relative to the location of these features.  For a seeps discussion in Boeing RFI  The available historical data suggests that SVOCs were not previously present in groundwater  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. (1985 data at RS‐15, RS‐17, 2008‐2009 data at PZ‐050). NFA Vadose zone to groundwater transport modeling predictions indicate the  two SVOCs identified as potentially being associated with sources in the  vadose zone (bis(2‐ethylhexyl)phthalate and di‐n‐octyl phthalate) will not  impact groundwater at concentrations above their GCLs at any time  during the 100 year simulation. For a data summary of individual SVOCs results in groundwater (that is, number of locations  sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in Appendix D. Page 1 of 5 DRAFT TABLE 4‐4 DQO Evaluation Findings for EEL RFI Site ‐ Groundwater and Seeps RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analytical  Group Study Question #3: Are data adequate to understand the fate and transport of  Study Question #4: Do concentrations of chemicals in groundwater  Study Question #2: Are the nature and extent of chemicals characterized to required  chemicals in groundwater, including volatilization of chemicals from  exceed action levels and/or do concentrations of chemicals present  RFI recommendation: NFA  characterization levels  in groundwater, or are data adequate to recommend the CUA cluster  groundwater to the vadose zone and migrations of chemicals to seeps and off‐ significant risk to current or future receptors (indoor air, seeps, or off‐ or CMS Assessment or portions of the CUA cluster for CMS? site wells, or are data adequate to recommend the CUA cluster or portions of  site wells)? the CUA cluster for CMS? Yes Yes No NFA Recent PAH data for the groundwater in and downgradient of the EEL RFI site are available.  Samples collected at wells PZ‐050 and RS‐37 were analyzed for PAHs in 2014 and samples  collected at downgradient wells ES‐29, and ES‐30 were analyzed for PAHs during one or more  of the following years: 2011, 2013, 2014. The available historical data includes 1985 data at RS‐ 15, RS‐17, and 2008 data at PZ‐028 and PZ‐050 and 2009 data at PZ‐050. PAHs A review of both historical and recent groundwater shows nearly all PAH data as below  detection limits with only fluoranthene and pyrene detected in 2013, with concentrations  below GCLs.  For a data summary of individual PAHs results in groundwater (that is, number of locations  sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in Appendix D. Energetics Petroleum  Hydrocarbons PAH data for groundwater at the EEL RFI site are available for 3 well locations in  the historical groundwater data (prior to 2010) and 4 wells in the recent (2010 to  2014) data. PAHs have not been detected historically or recently in groundwater  at the EEL RFI site with the exception of low concentrations (below GCL) of  fluoranthene and pyrene detected at ES‐30 in 2013. Sampling to date has not  shown PAHs to be a prevalent contaminant in groundwater. PAHs have not been detected historically or recently at or above GCLs in  groundwater at EEL. Vadose zone to groundwater transport modeling predictions indicate  PAHs will not impact groundwater at concentrations above their GCLs at  any time during the 100 year simulation. Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  consequence in light of its distant location from, and magnitude of releases,  relative to the location of these features. For a seeps discussion in Boeing RFI  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. Yes Yes Recent perchlorate data for the groundwater in and downgradient of the EEL RFI site are  available. Samples collected at PZ‐050 were analyzed for perchlorate in 2014. Results showed  a detection at 0.83 ug/L which is below the GCL (California MCL) of 6 ug/L. The available  historical data includes 1997 data at ES‐30, 1998 data at ES‐23, ES‐28, ES‐29, ES‐30, RS‐15, and  RS‐17, and 2003 data at RS‐15, RS‐17, PZ‐038, and PZ‐051. Of the historical data, perchlorate  was detected in 2003 at PZ‐038 and PZ‐051 but concentrations were below the GCL.  For a data summary of individual perchlorate results in groundwater (that is, number of  locations sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in  Appendix D. Perchlorate data for groundwater at the EEL RFI site are available for 7 well  Perchlorate has not been detected historically or recently at or above its  However, perchlorate is  locations in the historical groundwater data (prior to 2010) and one well, PZ‐050,  GCL in groundwater at the EEL RFI site. recommended for CMS in  in the recent (2010 to 2014) data. Perchlorate has not been detected in  the vadose zone for  groundwater in and downgradient of EEL above its GCL.  Vadose zone to groundwater transport modeling predictions indicate  protection of  perchlorate will impact groundwater at concentrations above its GCL  groundwater.  Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  during the 100 year simulation and the groundwater protection  Groundwater monitoring  consequence in light of its distant location from, and magnitude of releases,  evaluation indicates perchlorate concentrations in vadose zone samples  every 5 years for the  relative to the location of these features. For a seeps discussion in Boeing RFI  collected at the EEL RFI site are in exceedance of vadose zone  arrival of perchlorate in  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. concentrations protective of groundwater. groundwater is  recommended. Yes Yes Yes  Recent TPH data for the groundwater at and near the EEL RFI site are available. Samples  collected at EEL wells PZ‐050 and RS‐37 were analyzed for petroleum hydrocarbons. Results  showed detections above GCLs at PZ‐050 and detections below the detection limit (ND) at RS‐ 37. Downgradient wells ES‐30 and ES‐29 were sampled and analyzed for petroleum  hydrocarbons during one or more of the following years: 2011, 2013, 2014. Samples from ES‐ 30 had DRO concentrations detected above the GCL in 2013, where other sampling results  showed concentrations below the detection limit (ND). The available historical data includes  1998 data at ES‐28, ES‐30, and RS‐15, and 2008 and 2009 data at PZ‐050. Results from these  events show concentrations below the reporting limit (ND). No statistically significant concentration trends for petroleum hydrocarbons in  groundwater at and downgradient of the EEL RFI site were identified during  trend analysis (Appendix D). Concentrations have exceeded GCLs, but the concentrations do not  present a significant risk to future receptors based on constiuent  chemicals (PAHs and BTEX).  No Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  consequence in light of its distant location from, and magnitude of releases,  relative to the location of these features. For a seeps discussion in Boeing RFI  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. The TPH groundwater plume extends from the northeastern edge of EEL at PZ‐050 into  Compound A.  NFA NFA There are not suffficient  data indicating DRO is  present above its GCL in  groundwater at the EEL RFI  site, thus continued  Concentrations of DRO were above GCLs at wells ES‐30 and PZ‐050  during 2013 and 2014 sampling. The elevated detections of DRO at wells  monitoring for DRO in  ES‐30 and PZ‐050 are limited to one event at each well, and the elevated  groundwater at the EEL RFI  DRO at PZ‐050 occurred during a sampling event where deviations from  site is recommended. the typical sampling procedures occurred due to an insufficient water  column. The vadose zone transport modeling groundwater protection evaluation  for DRO indicates concentrations in vadose zone samples collected at the  EEL RFI site are not in exceedance of vadose zone concentrations  protective of groundwater. Vadose zone to groundwater transport  modeling predictions for ODRO, identified as a source in the vadose zone  but not present in groundwater above its GCL, indicate it will not impact  groundwater at concentrations above its GCL at any time during the 100  year simulation. For a data summary of individual TPH results in groundwater (that is, number of locations  sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in Appendix D. Page 2 of 5 DRAFT TABLE 4‐4 DQO Evaluation Findings for EEL RFI Site ‐ Groundwater and Seeps RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analytical  Group PCBs Study Question #3: Are data adequate to understand the fate and transport of  Study Question #4: Do concentrations of chemicals in groundwater  Study Question #2: Are the nature and extent of chemicals characterized to required  chemicals in groundwater, including volatilization of chemicals from  exceed action levels and/or do concentrations of chemicals present  RFI recommendation: NFA  characterization levels  in groundwater, or are data adequate to recommend the CUA cluster  groundwater to the vadose zone and migrations of chemicals to seeps and off‐ significant risk to current or future receptors (indoor air, seeps, or off‐ or CMS Assessment or portions of the CUA cluster for CMS? site wells, or are data adequate to recommend the CUA cluster or portions of  site wells)? the CUA cluster for CMS? Yes Yes No NFA Recent PCB data for the groundwater at the EEL RFI site are available. Samples collected at  wells PZ‐050 and RS‐37 in 2014 were analyzed for PCBs. Concentrations were below the  detection limit (ND) for all PCBs and both well locations. Nearby well ES‐29 was also sampled  in 2014 and results were consistent with the above. PCBs have low water solubility and high soil‐water partitioning coefficients thus  PCBs have not been detected in groundwater at or near EEL. they are relatively immobile. Sampling to date has not shown PCBs to be a  prevalent contaminant in groundwater at SSFL. Further, recent (2014) sampling  Vadose zone to groundwater transport modeling predictions indicate  PCBs will not impact groundwater at concentrations above their GCLs at  at the EEL RFI site shows no detections of PCBs in groundwater at the RFI site.  any time during the 100 year simulation. For a data summary of individual PCBs results in groundwater (that is, number of locations  Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in Appendix D. consequence in light of its distant location from, and magnitude of releases,  relative to the location of these features. For a seeps discussion in Boeing RFI  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. Yes Yes.  Recent herbicide data for the groundwater at and near the EEL RFI site are available. Samples  Herbicides were not detected in groundwater at the EEL RFI site during recent  collected at wells ES‐29 and RS‐37 in 2014 were analyzed for herbicides. Results showed no  2014 sampling. Site‐wide sampling to date has not shown herbicides to be a  detections.  prevalent contaminant in groundwater at SSFL. Herbicides Pesticides No.  NFA Herbicides have not been detected in groundwater at the EEL RFI site.  However, 2,4‐‐ Dichlorophenoxybutyric  Acid and MCPA are  recommended for CMS in  the vadose zone for the  future protection of  groundwater.  Groundwater monitoring  every 5 years for the  arrival of these herbicides  in groundwater is  recommended. Vadose zone to groundwater transport modeling predictions indicate 2,4‐ Dichlorophenoxybutyric Acid and MCPA will impact groundwater at  concentrations above their GCLs during the 100 year simulation and the  groundwater protection evaluation indicates 2,4‐Dichlorophenoxybutyric  Acid and MCPA concentrations in vadose zone samples collected at the  EEL RFI site are in exceedance of vadose zone concentrations protective  of groundwater. For a data summary of individual herbicides results in groundwater (that is, number of  locations sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in  Appendix D. Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  consequence in light of its distant location from, and magnitude of releases,  relative to the location of these features. For a seeps discussion in Boeing RFI  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. Yes Yes Recent pesticide data for the groundwater at and near the EEL RFI site are available. Samples  collected at wells ES‐29, PZ‐050 and RS‐37 in 2014 were analyzed for pesticides. Results  showed no detections. Pesticides were not detected in groundwater at the EEL RFI site during recent  Pesticides have not been detected in groundwater at the EEL RFI site.  2014 sampling, and site‐wide sampling to date has not shown pesticides to be a  prevalent contaminant in groundwater at SSFL.  Vadose zone to groundwater transport modeling predictions indicate  beta‐BHC, heptachlor, and heptachlor epoxide will impact groundwater  Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  at concentrations above their GCLs during the 100 year simulation and  consequence in light of its distant location from, and magnitude of releases,  the groundwater protection evaluation indicates beta‐BHC, heptachlor,  relative to the location of these features. For a seeps discussion in Boeing RFI  and heptachlor epoxide concentrations in vadose zone samples collected  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. at the EEL RFI site are in exceedance of vadose zone concentrations  protective of groundwater. For a data summary of individual pesticides results in groundwater (that is, number of  locations sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in  Appendix D. No Page 3 of 5 NFA However, beta‐BHC,  heptachlor, and heptachlor  epoxide are recommended  for CMS in the vadose  zone for the future  protection of  groundwater.  Groundwater monitoring  every 5 years for the  arrival of these pesticides  in groundwater is  recommended. DRAFT TABLE 4‐4 DQO Evaluation Findings for EEL RFI Site ‐ Groundwater and Seeps RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analytical  Group Study Question #3: Are data adequate to understand the fate and transport of  Study Question #4: Do concentrations of chemicals in groundwater  Study Question #2: Are the nature and extent of chemicals characterized to required  chemicals in groundwater, including volatilization of chemicals from  exceed action levels and/or do concentrations of chemicals present  RFI recommendation: NFA  characterization levels  in groundwater, or are data adequate to recommend the CUA cluster  groundwater to the vadose zone and migrations of chemicals to seeps and off‐ significant risk to current or future receptors (indoor air, seeps, or off‐ or CMS Assessment or portions of the CUA cluster for CMS? site wells, or are data adequate to recommend the CUA cluster or portions of  site wells)? the CUA cluster for CMS? Yes Yes No NFA Recent dioxins and furans data for the groundwater at and downgradient of the EEL RFI site  Dioxins and furans have low water solubility and high soil‐water partitioning  are available. Samples collected at wells ES‐29, ES‐30, PZ‐050 and RS‐37 in 2014 were analyzed  coefficients thus they are relatively immobile. Sampling to date has not shown  the EEL RFI site to be a source of dioxins and furans to groundwater.  Dioxins and  for dioxins and furans. Results show no detections above GCLs. Furans For a data summary of individual dioxins and furans results in groundwater (that is, number of  Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  locations sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in  consequence in light of its distant location from, and magnitude of releases,  Appendix D. relative to the location of these features. For a seeps discussion in Boeing RFI  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. Metals Yes Yes Antimony, arsenic, barium, beryllium, cadmium, hexavalent chromium, manganese, mercury,  silver, and sodium were identified as potential sources in the vadose zone. These metals were  analyzed at 6 well locations interpreted to monitor the EEL RFI site in recent data (2010 to  2014) and at 3 locations in historical data (prior to 2010). ‐ Cadmium was detected above its GCL in both recent and historical data.   ‐ Manganese was detected above its GCLs in recent data.   ‐ Antimony, arsenic, barium, beryllium, hexavalent chromium, mercury, silver, and sodium  were not detected or detected below their GCLs. Metals have been detected above GCLs historically and recently. Review of the  recent groundwater data (2010 to 2014) at and surrounding EEL indicates that  metals that are potentially sourced from EEL that are also exceeding in  groundwater (manganese and cadmium) are localized to one well location, PZ‐ 050. The metals that are present in groundwater above GCLs at EEL are near or  only slightly above the screening values.  Dioxins and furans have not been detected in groundwater at or near the  EEL RFI site. Vadose zone to groundwater transport modeling predictions indicate  dioxins and furans will not impact groundwater at concentrations above  their GCLs at any time during the 100 year simulation. Yes NFA Metals have been detected above GCLs historically and recently but  There are not suffficient  concentrations are relatively low in groundwater at the EEL RFI site, and a  data indicating cadmium  review of surrounding and down‐gradient wells shows that the metals in  and manganese are  groundwater potentially sourced from the EEL RFI site are localized to  present above their GCLs  one well. The elevated detections of cadmium and manganese occurred  in groundwater at the EEL  at PZ‐050 during the sampling event where the standard sampling  RFI site, thus continued  procedures were not followed and the results have not been verified  monitoring for these  Given the relatively low concentration and localized nature of the metals at EEL,  with a successive sampling event (see Appendix D for further details). metals in groundwater at  migration to seeps and offsite wells is insignificant. For a seeps discussion in  the EEL RFI site is  Other metals with exceedances of their screening levels in groundwater but not in the vadose  Boeing RFI Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. The vadose zone transport modeling groundwater protection evaluation  recommended.  zone include boron, copper, lithium, molybdenum, nickel, potassium, selenium, strontium,  indicates that barium, cadmium, manganese, mercury, and silver  Groundwater monitoring  thallium, and vanadium.  The recent (2010 to 2014) and historical data (prior to 2010)  concentrations in vadose zone samples collected at the EEL RFI site are  every 5 years for the  available for these metals showed the following: not in exceedance of vadose zone concentrations protective of  arrival of barium, mercury,  ‐  Copper, selenium, and vanadium were detected above their GCLs in both recent and  groundwater, but that sodium concentrations are. Vadose zone to  silver, and sodium in  historical data.   groundwater transport modeling predictions for metals identified as  groundwater is also  ‐ Chromium, lithium, molybdenum, nickel, and thallium were detected above their GCLs in  sources in the vadose zone but not present in groundwater above their  recommended. recent data.   GCLs indicate that antimony, arsenic, beryllium, and hexavalent  ‐  Boron, potassium, and strontium were detected above their GCLs in historical data. chromium will not impact groundwater at concentrations above their  Evaluations of chemical use and sampling results indicate that these metals detections at  GCLs based on soil concentrations at the EEL RFI site during the 100 year  these well locations are not interpreted to be sourced from the EEL RFI site and could be  simulation, but that barium, mercury, silver, and sodium will. either the result from transport from adjacent RFI sites or representative of background as  concentrations are only slightly above GCLs. For a data summary of individual metals results in groundwater (that is, number of locations  sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in Appendix D. Page 4 of 5 DRAFT TABLE 4‐4 DQO Evaluation Findings for EEL RFI Site ‐ Groundwater and Seeps RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analytical  Group Study Question #3: Are data adequate to understand the fate and transport of  Study Question #4: Do concentrations of chemicals in groundwater  Study Question #2: Are the nature and extent of chemicals characterized to required  chemicals in groundwater, including volatilization of chemicals from  exceed action levels and/or do concentrations of chemicals present  RFI recommendation: NFA  characterization levels  in groundwater, or are data adequate to recommend the CUA cluster  groundwater to the vadose zone and migrations of chemicals to seeps and off‐ significant risk to current or future receptors (indoor air, seeps, or off‐ or CMS Assessment or portions of the CUA cluster for CMS? site wells, or are data adequate to recommend the CUA cluster or portions of  site wells)? the CUA cluster for CMS? Yes Yes No NFA Fluoride and nitrate were identified as potential sources in the vadose zone at the EEL RFI site.  Recent inorganics data for the groundwater at and near the EEL RFI site are available. Samples  collected at RS‐15 in 2012, ES‐29 in 2010‐2014, and ES‐28 in 2012 were analyzed for  inorganics. Results showed no detections above GCLs. Historical data showed nitrate‐NO3  exceeded its GCL at 3 well locations interpreted to monitor the EEL RFI site. Inorganics Impacts to seeps or off‐site wells from the EEL RFI site are of little to no  consequence in light of its distant location from, and magnitude of releases,  For a data summary of individual fluoride and nitrate results in groundwater (that is, number  relative to the location of these features. For a seeps discussion in Boeing RFI  of locations sampled/analyzed, number of results, and maximum result), refer to Table D‐1 in  Subarea 5/9 South, refer to the STL‐IV RFI site DSFR. Appendix D. Abbreviations Benzene hexachlorocyclohexane BHC DB Dichlorophenoxybutyric Acid CUA chemical use area CMS corrective measures study DCE EEL GCLs NFA ND RFI TBD TCE VOCs SVOCs Sampling to date has not shown inorganics to be a prevalent contaminant in  groundwater at SSFL. Further, recent sampling at wells near the EEL RFI site  shows no detections of inorganics above GCLs in groundwater.  dichloroethene Environmental Effects Laboratory groundwater characterization levels no further action Not detected above the method detection limit RCRA facility investigation to be determined trichloroethene volatile organic compounds semi‐volatile organic compounds Inorganics have not been detected above GCLs in groundwater near EEL.  However, nitrate is  recommended for CMS in  Vadose zone to groundwater transport modeling predictions indicate  the vadose zone for the  fluoride and nitrate will impact groundwater at concentrations above  future protection of  their GCLs during the 100 year simulation. The groundwater protection  groundwater.  evaluation indicates fluoride concentrations in vadose zone samples  Groundwater monitoring  collected at the EEL RFI site are not in exceedance of vadose zone  every 5 years for the  concentrations protective of groundwater, but that nitrate  arrival of fluoride and  concentrations are. Nitrate was predicted to reach groundwater at  nitrate in groundwater is  concentrations above its GCL at approximately 2 years and then decrease  recommended. (Appendix C). These modeling results combined with available  groundwater data at EEL indicate that nitrate concentrations reached  maximum concentrations during the historical time frame (prior to 2010)  and are now below GCLs, correlating with model predictions. References: CH2MHILL. 2015. Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Venture County, California. February 10. MWH. 2009. Draft Site‐Wide Groundwater Remedial Investigation Report,  Santa Susana Field Laboratory, Ventura County, California. Volumes 1 through  7.   In Association with the SSFL Groundwater Advisory Panel, University of Guelph,  Haley & Aldrich and AquaResource Inc. December. Page 5 of 5 DRAFT TABLE 5‐1 Human Health Risk Estimates RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Excess Lifetime Cancer Risk Noncancer Hazard Index 4E‐04 2 Site Soil 0 to 10 ft bgs Direct Contact 3E‐04 1 Background Soil Direct Contactb Incremental Risk for Soil Contactc Soil Vapor (Indoor Air Pathway) 2E‐04 3E‐04 3E‐05 0.5 2 7 Recreational Scenario Site Soil 0 to 2 ft bgs Direct Contact 1E‐04 0.4 Exposure Scenario Suburban Residential Scenario Site Soil 0 to 2 ft bgs Direct Contact b Primary Contributors to Cancer Riska Primary Contributors to Hazard Indexa Arsenic (ELCR=4E‐4, 97%) Benzo[a]pyrene (ELCR=5E‐6, 1%) 2,3,7,8‐TCDD TEQ (ELCR=4E‐6, 1%) Arsenic (ELCR=3E‐4, 97%) 2,3,7,8‐TCDD TEQ (ELCR=5E‐6, 2%) Benzo(a)pyrene (ELCR=2E‐6, <1%) Arsenic (ELCR=2E‐4, >99%) Arsenic (HQ=1, 67%) Trichloroethene (ELCR=3E‐5, 94%) Benzene (ELCR=2E‐6, 6%) Trichloroethene (HQ=7, >99%) Arsenic (ELCR=1E‐4, 96%) Benzo(a)pyrene (ELCR=2E‐6, 2%) Arsenic (ELCR=4E‐5, >99%) Exceeds Hot Spot Criteriond Arsenic, 2,3,7,8‐TCDD TEQ,  Benzo(a)pyrene None identified None identified None identified None identified 4E‐05 0.1 None identified Background Soil Direct Contact 7E‐05 0.3 Incremental Risk for Soil Contactc Notes: a  Primary contributors to the total risk are listed when chemical‐specific risk > 10‐6. Primary contributors to the hazard index (HI) are listed when HI > 1.  b  Background risk is based on data from the Final Chemical Soil Background Study Report (DTSC, 2012). c  Incremental risk is calculated as the site risk minus the background risk. For the suburban resident, the higher risk of 0 to 2 ft bgs or 0 to 10 ft bgs is used in the calculation. d  The highest risk well point within Boeing RFI Subarea 5/9 South is listed. bgs = below ground surface ELCR = excess lifetime cancer risk ft = feet HQ = hazard quotient TEQ = 2,3,7,8‐TCDD toxicity equivalents EEL_DSFR_Table_5‐1_5‐2.xlsx 1 of 1 TABLE 5‐2 Ecological Risk Estimates RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Hermit Thrush (0‐2 ft bgs)  Matrix Type  ERA Class SOIL Chemicals of Potential Ecological  Concern with Receptor HQs>1 Low  EcoRBSL  HQ Deer Mouse (0‐6 ft bgs) High  Low  EcoRBSL  Low INCR  High INCR  EcoRBSL  HQ HQ HQ HQ High  EcoRBSL  Low INCR  High INCR  HQ HQ HQ Weight of Evidence INCR HQ  INCR HQ  Exceeds  Exceeds  High  Potential  Low  EcoRBSL Hotspot EcoRBSL COEC COEC Depth  Interval Notes Measured Data Soil I Inorganics Soil I Inorganics Antimony Arsenic ‐‐ <1 ‐‐ <1 ‐‐ <1 ‐‐ <1 1E+01 8E+00 <1 <1 7E+00 3E+00 <1 <1 Yes Yes No No No No No No ‐‐ ‐‐ Incremental HQ<1 at High EcoRBSL. Incremental HQ<1 at High EcoRBSL. Soil I Inorganics Hexavalent Chromium ‐‐ ‐‐ ‐‐ ‐‐ <1 <1 <1 <1 No No No No ‐‐ Incremental HQ<1 at High EcoRBSL. Soil O Dioxins and Furans Dioxins and Furans TEQ for Birds 2E+00 <1 2E+00 <1 ‐‐ ‐‐ ‐‐ ‐‐ Yes No No No ‐‐ Soil O Dioxins and Furans Dioxins and Furans TEQ for Mammals ‐‐ ‐‐ ‐‐ ‐‐ 3E+01 3E+00 3E+01 3E+00 Yes Yes Yes Yes 0‐6 ft Incremental HQ >1 at the  High EcoRBSL for  mammals only. Samples contributing to risk  extend to 6ft bgs. <1 2E+00 ‐‐ <1 <1 <1 ‐‐ <1 8E+00 <1 2E+00 <1 7E+00 <1 <1 <1 Yes Yes No No No No No No ‐‐ ‐‐ Incremental HQ<1 at High EcoRBSL. Incremental HQ<1 at High EcoRBSL. bkg No WOE No No WOE ‐‐ Chemical was never detected, but was  retained for evaluation because SQLs  exceeded the Low EcoRBSL (SQL Screen). No  exceedances of the High EcoRBSL. Soil O Herbicides Soil O Pesticides Non‐Detect (SQL Screen) Data Soil O Aroclors MCPA 4,4'‐DDT Aroclor 1248 <1 <1 bkg bkg 4E+00 <1 bkg No Extrapolated Data Soil O PCBs PCB TEQ for Birds Soil O PCBs PCB TEQ for Mammals 3E+01 3E+00 3E+01 3E+00 ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes No No WOE ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7E+01 7E+00 6E+01 6E+00 Yes Yes No No WOE ‐‐ Incremental HQ>1 , however, extrapolated  data are not used for risk management  decisions. Results for Dioxins Furans TEQs used for CMS  recommendations. Incremental HQ>1 , however, extrapolated  data are not used for risk management  decisions. Results for Dioxins and Furans TEQs used for  CMS recommendations. Hazard Indices Incremental HQ >1 at the  High EcoRBSL for  mammals only. Samples contributing to risk  extend to 6ft bgs. Potential hotspot. Soil O Dioxins and Furans Dioxins and Furans TEQ 2E+00 <1 2E+00 <1 3E+01 3E+00 3E+01 3E+00 Yes Yes Yes Yes 0‐6 ft Soil O Pesticides OC Pesticide HI 2E+00 <1 <1 <1 <1 <1 <1 <1 No No No No ‐‐ Incremental risk HQ <1 at High EcoRBSL. Trichloroethene ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 4E‐01 bkg bkg Yes No ‐‐ No ‐‐ Site risk HQ <1 at High EcoRBSL. SOIL VAPOR Soil Vapor VOC Notes:  ‐‐ = not applicable, not available bkg = background value was not available to calculate a background HQ CPEC = chemical of potential ecological concern ft bgs = feet below ground surface HI = hazard index HQ = hazard quotient INCR = incremental risk PCB = polychlorinated biphenyl SQL = sample quantitation limit TEQ = toxicity equivalent WOE = weight of evidence bold = site or incremental HQ>1 shading = retained as a COEC EN0411151012BAO  PAGE 1 OF 1 TABLE 6‐1 CMS Area Recommendations RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County,  California CMS Area/Location Depth (feet) Risk Drivers EEL‐CMS‐S1 1 Arsenic, dioxins and furans TEQ for mammals EEL‐CMS‐S2 2 Arsenic EEL‐CMS‐S3 1 Arsenic EEL‐CMS‐S4 2 Benzo(a)pyrene EEL‐CMS‐S5 1 Dioxins and furans TEQ for mammals EEL‐CMS‐S6 7 Dioxins and furans TEQ for mammals EEL‐CMS‐S7 1 Dioxins and furans TEQ for mammals EEL‐CMS‐S8 1 Dioxins and furans TEQ for mammals EEL‐CMS‐S9 3 Dioxins and furans TEQ for mammals EEL‐CMS‐SV1 6 TCE EEL‐CMS‐SV2 6 TCE, benzene EEL‐CMS‐VZ1 ‐‐ TCE, perchlorate EEL‐CMS‐VZ2 ‐‐ TCE, 2,4‐dichlorophenoxybutyric acid, heptachlor epoxide ELBS2000 ‐‐ Beta‐BHC, heptachlor, MCPA SL‐143‐SA5C ‐‐ Perchlorate, MCPA ELBS2035 ‐‐ Nitrate‐NO3 Notes: Soil and soil vapor CMS areas are based on the human health and ecological risk assessments provided in Appendix E, including the separate analysis of  additional DOE data provided in Appendix E4.  Vadose zone CMS areas are based on the vadose zone to groundwater transport modeling presented in Appendix C, including the separate analysis of  additional DOE data provided in Attachment C‐5 to Appendix C. CMS areas are also recommended for TCE and cis‐1,2‐DCE in groundwater at the EEL RFI site based on evaluation of the source zone, nature and extent, and  fate and transport of chemicals in groundwater.  ‐‐ = not applicable BHC = benzene hexachlorocyclohexane CMS = corrective measures study DCE = dichloroethene EEL = Environmental Effects Laboratory MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid TCE = trichloroethene TEQ = toxicity equivalent EN0317151003RDD PAGE 1 OF 1 Figures VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV UNDEVELOPED LAND UNDEVELOPED LAND LEGEND B-1 LA D UN EV O EL PE IEL Boeing RFI Subarea 1B North ND A1LF APTF D AREA IV ECL EEL LETF/CTL-1 Boeing RFI Subarea 5/9 North Canyon Silvernale AREA I AREA II AREA III Boeing RFI Subarea 1A North B359 HVN HVS Boeing RFI Subarea 1A Central DOE AOC Boundary NASA AOC Boundary RFI Group Boundary Administrative Boundary Ponds Boeing RFI Site Paved Road Dirt Road Unpaved trail R-1 Pond STP-3 Compound A Bowl Area STL-IV CTL-V CTL-III Area I Burn Pit Boeing RFI Subarea 5/9 South Boeing RFI Subarea 1B Southwest UNDEVELOPED LAND Boeing RFI Subarea 1A South Perimeter Pond Boeing RFI Subarea 1B Southeast Note: Investigations of former operational areas administered by NASA and DOE are being performed under agreed-upon AOCs with those parties. Therefore, RFI sites for NASA and DOE-administered areas are not presented in this figure. $ Boeing RFI Subarea 10 DRAFT 0 750 1,500 Feet 1 in = 1,500 ft FIGURE 1-1 Boeing RFI Subareas RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE1-1_SUBAREAS.MXD RANHORN 5/22/2015 3:49:04 PM Tanks Transformer Hazardous Materials Storage Pad Cryogenic Test Cell (Building 3271) Transformer Cryogenic Test Cell (Building 3108) Tank IV ea II r I A ve ea i r t A a str tive i n mi stra Ad ini m Ad Mechanics Workshop (Buildings 3227 and 3264) Cryogenic Laboratory (Building 3268) Office Building (Building 3905) Storage (Buildings 3109 and 3908) 0 North 50 100 Approximate scale in feet Source: CH2M HILL, 2012. SSFL Sitewide Gold Copy GIS Mapping and Analytical Geodatabase System (hard-drive deliverable). May, 2007 Note: 1) Portions of the EEL RFI Site located within Administrative Area IV are being characterized by US DOE. 2) The border between Administrative Areas III and IV is approximate. ES012313173936SCO SSFL_EEL_figure_Paik.ai 4/15 DRAFT FIGURE 2-1 2007 Aerial Photo of EEL RFI Site RCRA Facility Inves ga on, Data Summary and Findings Report, Environmental Effects Laboratory RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV 6 5 UNDEVELOPED LAND 17 16 7 3271 8 1 BASEMAP LEGEND Dirt Road Paved Road RFI Group Boundary Boeing RFI Site 9 13 3227 3271 EEL 12 14 3264 2 EEL RFI Site Reporting Area Pond 1 CUA Reference Number Transformer Pad ! ! ! ! ! ! Structure ! ! ! ! ! ! ! ! ! ! ! ! Aboveground Storage Tank Underground Storage Tank Not Yet Determined CUA Cluster (CC) 3 A B 3108 3109 Rock Outcrop Chemical Use Area (CUA) 3268 10 11 Administrative Boundary Potential CUA Storage Yard Potential CUA ID Debris Area Features ' ­ Debris Point A 3905 Disturbed Soil Vegetation Clearing ! Transformer Pole ! 3908 Pipeline 3600 Leach Field Line 175 0 Excavation Area U U U U UUndefined UUUUU UUUUU Feature Spray Field Debris Line Leach Field Area Drainage Channel Septic Tank Operational Channel 3252 Sumps 15 Former Ranch House 3251 Note: 1) Portions of EEL RFI Site located within Administrative Area IV are being characterized by US DOE. 2) Descriptions of the CUAs are presented in Table 3-2. 3) PCUA(s) presented in this figure were identified during the DQO evaluation, but were not carried forward as CUAs based on screening-level samples. 4) CUA 4 is an office building (Building 3905, but also referenced as Building 3805 in some historical documents) that did not have any chemical uses. 3267 EEL CC 1 STP-3 $ 0 17 5 DRAFT 0 30 60 Feet 1 in = 60 ft 0 Compound A Eastern Forming Pit Western Forming Pit SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE3-1_CUAAREAS.MXD RANHORN 5/26/2015 2:17:08 PM 17 5 FIGURE 3-1 EEL RFI Site CUAs and CUA Clusters RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV UNDEVELOPED LAND LEGEND # * * # ! ( ! ( * # 3271 3271 3109 # * ! ( # * ! ( * # * # ! ( # * ! (# * *! # ( ! ( ! ( EEL-CMS-VZ2 # * 3227 3264 3268 * ## * ! ( > 2x RBSL to <= 10x RBSL > 10x RBSL to <= 100x RBSL > 100x RBSL Non-detect Soil Soil Vapor ( ! ( # * BASEMAP LEGEND Boeing RFI Site # * RFI Group Boundary EEL-CMS-SV1 ! ( * # ! ( Administrative Boundary # * * # EEL RFI Site Reporting Area 3905 Chemical Use Area (CUA) ! ( CUA Cluster (CC) ! ( 3908 ! ( 3600 Soil Vapor CMS Area 1 75 ! ( * # Vadose Zone CMS Area 0 Features Pipeline EEL-CMS-SV2 # * ! ( > CL < 2x RBSL ! ( # * ! ( <= CL * # * # ! ( # * * ! ( 3108 # * # * # * * # ! ( # * " ) ) " ) " ) " ) " ) " # * EEL ( #! * Drainage Channel 3252 Operational Channel EEL-CMS-VZ1 ! ( Dirt Road Paved Road Rock Outcrop Former Ranch House 3251 Pond 3267 ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Structure STP-3 # * EEL CC 1 DRAFT Feet 1 in = 60 ft FIGURE 4-1 Comparison of VOC Analytical Notes: 1) For the purpose of this figure, Soil Characterization Levels are Results to Characterization Levels for selected based on background values, Suburban Residential RBSLs, Soil and Soil Vapor from 0 to 10 feet EcologicalCompound RBSLs, and A MRLs. 2) For the purpose of this figure, Soil Vapor Characterization Levels are the lowest of applicable VaporEastern Below Ground Surface, EEL RFI Site Intrusion RBSLs and Ecological RBSLs. 3) All chemicals for which a Forming Pit 0 screening level exists are presented on this figure. 4) Portions of EEL RFI Site located within Administrative Area IV are being characterized 5 by US DOE. 5) CUA 4 is an office building (Building 3905, but also17 Western referenced as Building 3805 in some historical documents) that did not Forming Pitany chemical uses. have SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE4-1_0_10.MXD RANHORN 5/27/2015 3:42:58 PM 60 1 ! ( * # 30 0 75 # * $ 0 RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV UNDEVELOPED LAND LEGEND EEL 3271 EEL-CMS-VZ2 3227 3271 " ) ) " ) " ) " ) " ) " <= CL * Soil Soil Vapor 3264 > CL < 2x RBSL > 2x RBSL to <= 10x RBSL > 10x RBSL to <= 100x RBSL > 100x RBSL Non-detect ( BASEMAP LEGEND Boeing RFI Site 3268 RFI Group Boundary EEL-CMS-SV1 3108 Administrative Boundary EEL RFI Site Reporting Area 3109 3905 Chemical Use Area (CUA) CUA Cluster (CC) 3908 3600 Soil Vapor CMS Area 1 75 EEL-CMS-SV2 Vadose Zone CMS Area 0 Features Pipeline Drainage Channel 3252 Operational Channel EEL-CMS-VZ1 Dirt Road Paved Road Former Ranch House 3251 Rock Outcrop Pond 3267 ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Structure STP-3 EEL CC 1 DRAFT 60 Feet 1 in = 60 ft 1 FIGURE 4-2 Comparison of VOC Analytical Results Notes: 1) For the purpose of this figure, Soil Characterization Levels are to Characterization Levels for Soil selected based on background values, Suburban Residential RBSLs, and Soil Vapor Greater than 10 feet EcologicalCompound RBSLs, and A MRLs. 2) For the purpose of this figure, Soil Vapor Characterization Levels are the lowest of applicable VaporEastern Intrusion Below Ground Surface, EEL RFI Site RBSLs and Ecological RBSLs. 3) All chemicals for which a screening Forming Pit 0 level exists are presented on this figure. 4) Portions of EEL RFI Site located within Administrative Area IV are being characterized by US DOE. 5 17 5) CUA 4 is an office building (Building 3905, but also referenced as Western Building 3805 in some historical documents) that did not have any Forming Pit uses. chemical SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE4-2_GT_10.MXD RANHORN 5/26/2015 2:44:16 PM 30 0 75 * # $ 0 RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California VICINITY MAP UND UN D ED OP EL EV ED LOP EVE D LA N NASA ND LA AREA I AREA III AREA II AREA IV UNDEVELOPED LAND # * EEL-CMS-S7 EEL *# # * * # # * #* * * # # * # # * # ** # * # 3271 ## * * * # 3271 # * # * EEL-CMS-S3 * # *3108 # # * 3109 * # SL-143-SA5C * # # * * # # * * # RFI Group Boundary # * * # # * Administrative Boundary EEL RFI Site Reporting Area Chemical Use Area (CUA) # * EEL-CMS-S6 * # CUA Cluster (CC) Soil CMS Area 3600 Vadose Zone CMS Area 1 75 EEL-CMS-S8 * # EEL-CMS-S5 BASEMAP LEGEND Boeing RFI Site * # * # 3908 EEL-CMS-S4 # * # * * # 3905 # * LEGEND Soil * <= CL # * > CL to <= 2x RBSL # * > 2x RBSL to <= 10x RBSL # * > 10x RBSL to <= 100x RBSL # * > 100x RBSL # * Non-detect # EEL-CMS-S1 * # * # ELBS2000 ## * * * # # * * # * # # * * # # * #* * # EEL-CMS-S2 3227 3264 * # * *# # # * # * * # * # * # 3268 * # # * EEL-CMS-VZ2 Vadose Zone CMS Locations 0 Features Pipeline 3252 EEL-CMS-VZ1 Drainage Channel Operational Channel Dirt Road Paved Road Former Ranch House 3251 * # Rock Outcrop Pond 3267 * # * # #* * # # * * # ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Structure STP-3 EEL-CMS-S9 ELBS2035 EEL CC 1 DRAFT * # * # $ 0 30 Feet 1 in = 60 ft FIGURE 4-3 Comparison of Other Analytical Results to Characterization Levels A of this figure, Soil Characterization Levels are for Soil from 0 to 2 feet Below Notes: 1) Compound For the purpose Eastern selected based on background values, Suburban Residential RBSLs, Ecological RBSLs, and MRLs. 2) All chemicals except VOCs for which a Pit Ground Surface, EEL RFI Site Forming 1 750 * # # * ! * # # * # * #* * # 0 screening level exists are presented on this figure. 3) Portions of EEL RFI Site located within Administrative Area IV are being characterized by 5 US DOE. 4) CUA 4 is an office building (Building 3905, but also 1 7 Western referenced as Building 3805 in some historical documents) that did Forming notPit have any chemical uses. SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE4-3_0_2.MXD NYOUNG 5/26/2015 2:44:01 PM RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California 60 VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV UNDEVELOPED LAND EEL-CMS-S7 EEL 3271 * # # * * # * # SL-143-SA5C * # * # * # # * # * BASEMAP LEGEND Boeing RFI Site RFI Group Boundary EEL-CMS-S2 * # * ## # * * Administrative Boundary EEL RFI Site Reporting Area * # * # # * # * * # EEL-CMS-S1 3227 3264 3268 #3108 * 3109 # * # * EEL-CMS-VZ2 * # # * * # # * # * * # 3271 EEL-CMS-S3 # * # * * # * # # * * # ## * * LEGEND Soil * <= CL # * > CL to <= 2x RBSL # * > 2x RBSL to <= 10x RBSL # * > 10x RBSL to <= 100x RBSL # * > 100x RBSL # * Non-detect # # * # * EEL-CMS-S6 Chemical Use Area (CUA) 3905 CUA Cluster (CC) # * 3908 # * * ## * Soil CMS Area Vadose Zone CMS Area 3600 # * 1 75 Vadose Zone CMS Locations 0 EEL-CMS-S8 Features Pipeline EEL-CMS-S4 3252 # * ELBS2000 * # Drainage Channel EEL-CMS-VZ1 EEL-CMS-S5 Operational Channel Dirt Road Paved Road Former Ranch House 3251 Rock Outcrop Pond 3267 * # ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Structure STP-3 * ## * * # EEL-CMS-S9 ELBS2035 EEL CC 1 DRAFT # * * # # * 30 Feet 1 in = 60 ft 1 FIGURE 4-4 Comparison of Other Analytical Results to Characterization Levels A of this figure, Soil Characterization Levels are for Soil from 2 to 10 feet Below Notes: 1)Compound For the purpose Eastern selected based on background values, Suburban Residential RBSLs, Ecological RBSLs, and MRLs. 2) All chemicals except VOCs for which a Pit Ground Surface, EEL RFI Site Forming 0 75 # * $ 0 * # 0 screening level exists are presented on this figure. 3) Portions of EEL RFI Site located within Administrative Area IV are being characterized by 5 US DOE. 4) CUA 4 is an office building (Building 3905, but also 17 Western referenced as Building 3805 in some historical documents) that did Forming notPit have any chemical uses. SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE4-4_2_10.MXD RANHORN 5/26/2015 2:45:04 PM RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California 60 VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV UNDEVELOPED LAND LEGEND Soil * <= CL # * > CL to <= 2x RBSL # * > 2x RBSL to <= 10x RBSL # * > 10x RBSL to <= 100x RBSL # * > 100x RBSL # * Non-detect # EEL-CMS-S7 EEL EEL-CMS-VZ2 EEL-CMS-S2 3271 EEL-CMS-S1 3227 3271 3264 BASEMAP LEGEND Boeing RFI Site 3268 RFI Group Boundary EEL-CMS-S3 Administrative Boundary EEL RFI Site Reporting Area 3108 EEL-CMS-S6 3109 Chemical Use Area (CUA) 3905 CUA Cluster (CC) Soil CMS Area 3908 Vadose Zone CMS Area 3600 SL-143-SA5C 1 75 Vadose Zone CMS Locations 0 EEL-CMS-S8 Features Pipeline EEL-CMS-S4 3252 Drainage Channel EEL-CMS-VZ1 ELBS2000 EEL-CMS-S5 Operational Channel Dirt Road Paved Road Former Ranch House 3251 Rock Outcrop Pond 3267 ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Structure STP-3 EEL-CMS-S9 ELBS2035 EEL CC 1 DRAFT # * 1 in = 60 ft 1 FIGURE 4-5 Comparison of Other Analytical Results to Characterization Levels A of this figure, Soil Characterization Levels are for Soil Greater than 10 feet Below Notes: 1)Compound For the purpose Eastern selected based on background values, Suburban Residential RBSLs, Ecological RBSLs, and MRLs. 2) All chemicals except VOCs for which a Pit Ground Surface, EEL RFI Site Forming 0 screening level exists are presented on this figure. 3) Portions of EEL RFI Site located within Administrative Area IV are being characterized by 5 US DOE. 4) CUA 4 is an office building (Building 3905, but also 17 Western referenced as Building 3805 in some historical documents) that did Forming notPit have any chemical uses. SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE4-5_GT_10.MXD RANHORN 5/26/2015 2:46:49 PM 30 Feet 0 75 * # * ## * $ 0 RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California 60 ES-29 < ! < ! PZ-018A-E ES-30 PZ-030 < ! ES-28 PZ-029 PZ-050 < ! < ! < ! < ! EEL ES-23 < ! < ! < ! RS-15 WS-11 RS-17 PZ-038 RS-41 Basemap Not Detected ) Porewater ! ! Deformation Bands Structures Finer Grained Unit (shale/siltstone) Area in Which Finer Grained Unit May Be Discontinuous Path: U:\BoeingSantaSusana\MXD\Vadose Zone Mass Flux\ReportFigures\EEL\EEL_bedrock.mxd SSFL Area Boundary Boeing RFI Site Boundary CUA Cluster Area of Impacted Vadose Zone Bedrock ES-26 < ! < ! PZ-015A-G < < !! RD-55B !< ( Soil Vapor * Soil Groundwater Locations Groundwater Monitoring Location PZ-036 Faults > BTV or GCV <= BTV or GCV STL-IV ES-17 HAR-32 < ! < ! ES-27 RS-09 RS-33 RS-14 Please Note: The original version of this figure includes colorized features and shading. A black and white copy of the figure should not be used because it may not accurately represent the information presented. The area of impacted bedrock was estimated by reviewing available rock core pore water data in combination with surrounding soil vapor, soil, and groundwater data collected at the RFI Site. To project the area of impacted bedrock for areas where no rock core data was available, the other site data (soil, soil vapor,and groundwater) was reviewed considering the chemical concentrations relative to their screening values, the chemical properties, the depth of highest chemical concentrations relative to bedrock, and the vadose zone to groundwater transport modeling predictions for the area. < ! Trichloroethene Vadose Zone Results ± < ! 220 g Feet g < ! 110 g < ! GCL-likely a ss ocia ted with EEL >GCL-likely a ss ocia ted with EEL a nd/ ora dja centsite >GCL-im pa cted fr om s our ces othertha nEEL <=GCL No Da ta Loca tionoutside ofBoeing Adm inistr a tive Ar ea Res ultsa r e b a sed onr ecentda ta collected fr om 2010to 2014.I fno r ecentda ta wa sa va ila b le fora m onitor ing loca tion,the m os tr ecent histor ica lr esultwa sus ed. Res ultsforwellsouts ide ofthe Boeing Adm inistr a tive a r ea wer e included inthe eva lua tionforthe RFIs ite inca s es wher e wellsinter ceptflow pa thsa nd a r e inter pr eted to m onitora nd conta in gr oundwa terr epr esenta tive ofthe s ite. ▬ PZ 038 ! Ñ Equiva lentTr ichlor oethene I s oconcentr a tionContour s( ug/ L) Tr ichlor oethene >GCLof5ug/ L Ar ea ofI m pa cted V a dose Zone Bedr ock SoilV a porCM S Basemap Dr a ina ge Fa ults ! Defor m a tionBa nds Str uctur es PZF 039 a ined Unit inerGr ( sha le/ s iltstone) Ar ea inW hich FinerGr a ined UnitM a y Be Dis continuous 30 60 120 Feet Aer ia lphoto cir ca 1967 ES16 RS09 Boeing RFISite Bounda r y DRAFT CUACluster s SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA Adm inistr a tive Bounda r ies Ab b r evia tions GCL-Gr oundwa terCha r a cter iza tionLevel ug/ L-m icr ogr a m sperliter ES27 !< 0 1inch =60feet !< ± Areas of Impacted Groundwater 100 !< CLto <=2x RBSL Res identia lRBSLs ,Ecologica lRBSLs, >2x RBSLto <=10x RBSL a nd M RLs . >10x RBSLto <=100x RBSL 2)Forthe pur pose ofthisfigur e,Soil V a porCha r a cter iza tionLevelsa r e the >100x RBSL lowestofa pplica b le V a porI ntr usion NotDetected RBSLsa nd Ecologica lRBSLs . SoilV a por Soil < < ! VOCs Vadose Zone Results <=CL Com pound A The extent of TCE ingr oundwa tera b ove the gr oundwa tercha r a cter iza tionlevel ( GCL)of 5m icr ogr a m sperliter( ug/ L)a s pr es ented inthe 2014SSFLRepor tonAnnua lGr oundwa terM onitor ing ( M W H,2015)isshowninb lue. !< !< !< !< Please Note: The original version of this figure includes colorized features and shading. A black and white copy of the figure should not be used because it may not accurately represent the information presented. I nter pr eted is oconcentr a tioncontour sof equiva lenttr ichlor oethene ( TCE) ,which isa s um of TCEa nd m ola requiva lentsof its da ughterpr oducts ,ingr oundwa terb enea th the EELRFISite forthe 20082013tim efr am ear es howninna vy b lue.Equiva lent TCE concentr a tionswer e ca lcula ted b y conver ting detected r esultsof TCE da ughterpr oductsto TCE using m ola rm a ssa nd s um m ing the r esultsforTCE a nd itsda ughterpr oducts .The isoconcentr a tioncontourinter pr eta tionsa r e bas ed onva dos e zone soil va pora nd s oil m a tr ix s a m pling r es ults,cor r ective m ea s ur esstudy a r ea s ,estim a ted flow pa thsfr om the thr eedim ens iona l gr oundwa terflow m odel,a nd equiva lent TCE gr oundwa ters a m pling r esults.Additiona l infor m a tion on the equiva lentTCEisoconcentr a tioncontour sa nd thr eedim ensiona lplum e eva lua tionsa ta nd inthe vicinity ofthe EELRFISite is pr ovided inAppendix Bof the Sub a r ea 5/ 9South RCRAFa cility I nvestiga tionDa ta Sum m a r y a nd FindingsRepor t. ESTI M ATED FOOTPRI NTOFI M PACTEDGROUNDW ATER EELRFISI TE HAR32 Figur e 47 RS33 VICINITY MAP E LO P E VE D LAN D UN D NASA D ED EEL-CMS-SV1 UN DE N LA AREA I OP EL V AREA II AREA III AREA IV UNDEVELOPED LAND EEL-CMS-S7 BASEMAP LEGEND Boeing RFI Site EEL-CMS-VZ2 EEL-CMS-S2 3271 3227 3271 EEL 3264 3268 EEL-CMS-S6 EEL-CMS-S1 Drainage Channel EEL RFI Site Reporting Area Operational Channel CUA Cluster (CC) Dirt Road Paved Road Soil CMS Area Rock Outcrop Pond Vadose Zone CMS Area ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! Structure Vadose Zone CMS Locations 3108 Note: 1) Portions of EEL RFI Site located within Administrative Area IV are being characterized by US DOE. 3109 3905 C M S A re a / L o c a t io n D e p t h (f e e t ) R is k D riv e rs 3908 3600 SL-143-SA5C 175 0 EEL-CMS-SV2 3252 ELBS2000 Administrative Boundary Soil Vapor CMS Area EEL-CMS-S3 EEL-CMS-S8 EEL-CMS-S4 Features Pipeline RFI Group Boundary EEL-CMS-S5 EEL-CMS-VZ1 Former Ranch House 3251 3267 EEL CC 1 STP-3 EEL-CMS-S9 ELBS2035 E E L -C M S -S 1 1 A rs e n ic , d io xin s a n d f u ra n s T E Q f o r m a m m a ls E E L -C M S -S 2 2 A rs e n ic E E L -C M S -S 3 1 A rs e n ic E E L -C M S -S 4 2 B e n zo (a )p yre n e E E L -C M S -S 5 1 D io xin s a n d f u ra n s T E Q f o r m a m m a ls E E L -C M S -S 6 7 D io xin s a n d f u ra n s T E Q f o r m a m m a ls E E L -C M S -S 7 1 D io xin s a n d f u ra n s T E Q f o r m a m m a ls E E L -C M S -S 8 1 D io xin s a n d f u ra n s T E Q f o r m a m m a ls E E L -C M S -S 9 3 D io xin s a n d f u ra n s T E Q f o r m a m m a ls E E L -C M S -S V 1 6 TCE E E L -C M S -S V 2 6 T C E , b e n ze n e E E L -C M S -V Z 1 -- T C E , p e rc h lo ra t e E E L -C M S -V Z 2 -- T C E , 2 ,4 -D B , h e p t a c h lo r e p o xid e ELB S2000 -- B e t a -B H C , h e p t a c h lo r, M C P A S L -14 3 -S A 5 C -- P e rc h lo ra t e , M C P A ELB S2035 -- N it ra t e -N O 3 0 17 5 DRAFT 0 Compound A Eastern Forming Pit Western Forming Pit SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGURE6-1_CMS_NFA_AREAS.MXD RANHORN 5/26/2015 3:38:02 PM 17 5 $ 0 30 Feet 1 in = 60 ft FIGURE 6-1 Summary of CMS and NFA Area Recommendations, EEL RFI Site RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California 60 Appendix A Sample Locations and Analytical Data for EEL RFI Site ELBS3020 * ELBS1400 * ELBS2028 * *ELBS1401 ELBS2002 ELBS1028 ** ELBS04 * *ELBS13 ELBS1024 ELSV08 ELBS2009 * ( (ELSV2003 ELBS02 * ELSV2014 ( MH02072993 * ELBS2016 ** ELSV02 ( ELSV2012 ( ELSS01 *D-3-03 *ELBS05 * ELBS1403 ELBS14 * *ELBS1026 ELBS01 * 3271 ELBS1405 3271 * ELSV2016 ( ELBS2025 ** ELBS1006 * * * ELBS1019 ELBS3007 ELBS1005 * ELBS1018 * ELBS3011 ELBS2018 * * ELBS2024 ELSV3000 ( ELSV2004 ELBS2003 * ELBS1007 ELBS3015 * * ELBS10 * ELSV2011 ( ELBS2005 * ELBS1014 ELSV01 ( ELBS07 ELBS06 * * ELBS1402 * PZ-050 ELSV1004 > ! * ( * ELSV2013 ELBS1409 ( *ELBS2007 * STBS1019 3905 ELSV03 STBS3008 * ( 3908 ELSV1402 * * ELBS2015 A3_SED_DG-12 ELBS2022 (ELSV2000 * ELBS1410 0 * SL-143-SA5C 3600 ( ELBS1017 A3_SED_DG-11 ELBS2012 * (ELSV2018 * ( ELBS1016 * ELBS2010 * ELBS3006 * ELBS3012 * ELSV2002 ELBS3017 ELSV1403 ( * ELBS2004 ELSV2009 ( * * ELBS03 ELBS1011 ELBS2001 * * * ELSV2006 * * ( * * 3109 ELBS1021 ( ELBS1012 ELBS3002 ELSV2001 ELBS3008 ELBS1015 * *ELBS2017 * ( *ELBS2020 3108 ELBS1003 * ELBS1027 * *ELBS2006 3268 ELBS1013 * ELBS2026 3227 ELBS3001 ELBS1020 * ELBS1004 ELBS1029 * 3264 EEL ELBS3010 * 17 5 ** * VICINITY MAP ELSV1003 ELBS2021 ELSV1401 ( * E LO P E VE D LAN ELBS3000 ED ELBS2000 * ( UN GMBS2012A ELSV2008 A3_SED_DG-13 NASA D ( * D UN D 3252 DE N LA AREA I OP EL V AREA III AREA II AREA IV * * Former Ranch House UNDEVELOPED LAND 3251 ELSV1400 ( LEGEND Soil ( Soil Vapor > Groundwater ! 3267 * ELBS3009 * STP-3 Boeing RFI Site RS-37 > ! ELBS3021 * ELBS3004 RS-17 * * *ELBS3003 RFI Group Boundary ELBS3005 EEL RFI Site Reporting Area ELBS2008 > ! A3_SED_DG-14 BASEMAP LEGEND Pond Transformer Pad ! ! ! ! ! ! Administrative Boundary ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ** Aboveground Storage Tank Underground Storage Tank Not Yet Determined Features ' ­ Debris Point Storage Yard ! Transformer Pole ! * Pipeline Disturbed Soil Leach Field Line Vegetation Clearing Drainage Channel GMBS2012B * * Debris Area Debris Line ELBS2035 GMBS2012 ELBS2036 Operational Channel * ELBS2034 * (SWBS1006 * SWSV1006 ELBS3023 ELBS3024 Excavation Area UUUUU U U U U UUndefined UUUUU Feature Spray Field Dirt Road Paved Road Septic Tank Rock Outcrop Sump Leach Field Area 1) Portions of EEL RFI Site located within Administrative Area IV are being characterized by US DOE. 2) CUA 4 is an office building (Building 3905, but also referenced as Building 3805 in some historical documents) that did not have any chemical uses. 3) This figure presents locations of samples representative of current conditions at the EEL RFI site and evaluated in this EEL DSFR. * ELBS2023 Structure ELBS3016 ** * *ELBS3022 Compound A DRAFT $ 0 Eastern Forming Pit 15 Feet 1 in = 30 ft APPENDIX A1 Sample Locations at EEL RFI Site Western Forming Pit SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGUREA1_SAMPLELOCS_C.MXD RANHORN 5/28/2015 2:03:01 PM RCRA Facility Investigation Data Summary and Findings Report Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California 30 Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 Sample ID Sample Type Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Collection  Date 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 Sample  Bottom  Depth (feet bgs) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Calculated Result Calculated Result Calculated Result Calculated Result Confirmation Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Analysis  Method 1613B 1613B 1613B 8260B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8270C 8270C 8270C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal Xylenes, Total 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene Phosphorus Aluminum Antimony Barium Beryllium Boron Calcium Chromium Cobalt Iron Lithium Manganese Potassium Sodium Strontium Tin Titanium Vanadium Zinc Zirconium Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,2‐Diphenylhydrazine 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Carbazole Dibenzofuran Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorocyclopentadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine Page 1 of 108 CAS Number 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 1330207 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 121142 606202 98953 7723140 7429905 7440360 7440393 7440417 7440428 7440702 7440473 7440484 7439896 7439932 7439965 7440097 7440235 7440246 7440315 7440326 7440622 7440666 7440677 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 122667 95954 88062 120832 105679 51285 91587 88744 88755 91941 99092 534521 101553 7005723 100027 62533 92875 65850 100516 111911 111444 108601 117817 85687 86748 132649 84662 131113 84742 117840 118741 77474 67721 78591 62759 621647 86306 Result  Value 0.177 0.104 0.197 5 0.122 0.388 1.52 0.0836 0.108 0.0583 0.0965 0.571 0.879 0.807 0.253 0.173 0.107 0.123 0.0458 1.06 3.47 5.45 5.45 1.41 28.8 5.45 5.45 1.09 1.09 180 37 37 229 18100 0.795 113 0.756 8.2 2480 25.5 8.14 22400 19.3 550 3860 130 25.4 3.66 1320 45.9 54.4 3.72 6.51 0.316 17.6 8.83 0.961 22.9 0.218 0.0359 0.405 0.0104 5 5 37 37 37 37 37 1100 36 37 37 370 180 550 37 37 550 550 3700 550 550 37 37 37 190 180 37 37 180 180 180 180 19 550 180 37 180 37 37 Result  Value  Units ng/kg ng/kg ng/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.000000177 mg/kg 0.000000104 mg/kg 0.000000197 mg/kg 0.005 mg/kg 0.00000109 mg/kg 0.000000388 mg/kg 0.00000152 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.000000879 mg/kg 0.000000807 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000109 mg/kg 0.00000106 mg/kg 0.00000347 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000141 mg/kg 0.0000288 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000109 mg/kg 0.00000109 mg/kg 0.18 mg/kg 0.037 mg/kg 0.037 mg/kg 229 mg/kg 18100 mg/kg 2.15 mg/kg 113 mg/kg 0.756 mg/kg 8.2 mg/kg 2480 mg/kg 25.5 mg/kg 8.14 mg/kg 22400 mg/kg 19.3 mg/kg 550 mg/kg 3860 mg/kg 53.7 mg/kg 25.4 mg/kg 10.7 mg/kg 1320 mg/kg 45.9 mg/kg 54.4 mg/kg 3.72 mg/kg 6.51 mg/kg 0.316 mg/kg 17.6 mg/kg 8.83 mg/kg 0.961 mg/kg 22.9 mg/kg 0.218 mg/kg 0.0359 mg/kg 0.405 mg/kg 0.104 mg/kg 0.005 mg/kg 0.005 mg/kg 0.037 mg/kg 0.037 mg/kg 0.037 mg/kg 0.037 mg/kg 0.037 mg/kg 1.1 mg/kg 0.036 mg/kg 0.037 mg/kg 0.037 mg/kg 0.37 mg/kg 0.18 mg/kg 0.55 mg/kg 0.037 mg/kg 0.037 mg/kg 0.55 mg/kg 0.55 mg/kg 3.7 mg/kg 0.55 mg/kg 0.55 mg/kg 0.037 mg/kg 0.037 mg/kg 0.037 mg/kg 0.19 mg/kg 0.18 mg/kg 0.037 mg/kg 0.037 mg/kg 0.18 mg/kg 0.18 mg/kg 0.18 mg/kg 0.18 mg/kg 0.019 mg/kg 0.55 mg/kg 0.18 mg/kg 0.037 mg/kg 0.18 mg/kg 0.037 mg/kg 0.037 mg/kg Detected Y Y Y N N Y Y N N N N N Y Y N N N N N Y Y Y Y Y Y Y Y Y Y N N N Y Y N Y Y Y Y Y Y Y Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code U U J J U U U U UJ J J U UJ U U U J J J J J J J J J U U U Validation Note , F, F, B , F, F, B F, B F, B B F, B *DVR , F, B , F, B B *DVR F, F, B F, B , Original Result = 1.43 , Original Result = 2.04 , Original Result = 0.766 , Original Result = 1.21 , Original Result = 0.785 , Original Result = 0.162 U U F U B J J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.0000057 No 3.11E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 3.50E‐01 Background 3.4 No 1.47E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 37900 No 4.78E‐01 Background 0.5 Yes 4.30E+00 MRL 203.8 No 5.54E‐01 Background 4.8 No 1.58E‐01 Ecological RBSL 22 No 3.73E‐01 Ecological RBSL ‐‐ No SL No SL 60.11 No 4.24E‐01 Background 26.18 No 3.11E‐01 Background ‐‐ No SL No SL 64.4 No 3.00E‐01 Background 723 No 7.61E‐01 Background 7524 No 5.13E‐01 Background 754 No 7.12E‐02 Background 1210 No 2.10E‐02 Ecological RBSL 31 No 3.45E‐01 Ecological RBSL 1865 No 7.08E‐01 Background 111.8 No 4.11E‐01 Background 153 No 3.56E‐01 Background 10.64 No 3.50E‐01 Background 24.2 No 2.69E‐01 Background 0.435 No 7.26E‐01 Background 42 No 4.19E‐01 Background 33.9 No 2.60E‐01 Background 1.642 No 5.85E‐01 Background 64.2 No 3.57E‐01 Background 1 No 2.18E‐01 MRL 0.99 No 3.63E‐02 Ecological RBSL 0.761 No 5.32E‐01 Suburban Residential RBSL 0.87 No 1.20E‐01 Ecological RBSL 10 No 5.00E‐04 Ecological RBSL 0.022 No 2.27E‐01 Ecological RBSL ‐‐ No SL No SL 75 No 4.93E‐04 Ecological RBSL 7.43 No 4.98E‐03 Suburban Residential RBSL ‐‐ No SL No SL 65 No 5.69E‐04 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 8 No 6.88E‐02 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.5 No 1.22E‐01 Ecological RBSL 4.5 No 1.22E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.32 No 5.94E‐01 Ecological RBSL 90 No 2.00E‐03 Ecological RBSL 1.5 No 2.47E‐02 Ecological RBSL 1.2 No 3.08E‐02 Ecological RBSL 2.3 No 7.83E‐02 Ecological RBSL 4.5 No 4.00E‐02 Ecological RBSL 0.11 Yes 1.64E+00 Ecological RBSL 13 No 1.38E‐02 Ecological RBSL ‐‐ No SL No SL 3 No 1.83E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.0325 Yes 5.54E+00 Suburban Residential RBSL ‐‐ No SL No SL 2.3 No 1.61E‐02 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 5 1.09 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 1.09 5.45 5.45 5.45 5.45 10.9 10.9 5.45 5.45 1.09 1.09 180 37 37 10.7 10.7 2.15 0.537 0.268 5.37 10.7 0.805 0.537 10.7 2.1 0.537 53.7 53.7 0.537 10.7 1.07 0.537 2.15 5.37 0.43 0.107 0.215 0.215 0.107 0.43 0.43 0.107 0.107 0.104 5 5 37 37 37 37 37 1100 36 37 37 370 180 550 37 37 550 550 3700 550 550 37 37 37 190 180 37 37 180 180 180 180 19 550 180 37 180 37 37 ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 1 0.122 0.0251 0.051 0.0327 0.0237 0.0359 0.0219 0.0392 0.0254 0.0353 0.0208 0.042 0.0216 0.0187 0.0458 0.0284 0.051 0.0231 0.0367 0.0697 0.0646 0.0197 0.042 0.0423 0.0458 73 18 18 3.1 7.74 0.795 0.0354 0.0719 0.902 3.59 0.172 0.106 3.89 0.37 0.0891 8.96 17.9 0.0354 0.236 0.183 0.14 0.215 0.902 0.168 0.0494 0.103 0.0172 0.0537 0.0881 0.107 0.0279 0.0322 0.0104 1 2 18 18 18 18 18 330 8 18 18 110 73 180 18 18 180 180 770 180 180 18 18 18 73 73 18 18 73 73 73 73 4 180 37 18 73 18 18 MDL  Units ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 Sample ID Sample Type Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte o‐Cresol p‐Chloroaniline p‐Chloro‐m‐cresol p‐Cresol Pentachlorophenol Phenol p‐Nitroaniline 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran Page 2 of 108 CAS Number 95487 106478 59507 106445 87865 108952 100016 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 Result  Value 37 37 37 37 190 37 180 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 3.8 9.1 9.1 9.1 9.1 9.1 9.1 9.1 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 11 11 22 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 5 5 5 5 5 5 5 5 5 5 5 5 5 55 5 5 5 5 5 5 5 5 5 0.112 0.0251 0.195 0.422 1.82 0.373 0.264 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.037 mg/kg 0.037 mg/kg 0.037 mg/kg 0.037 mg/kg 0.19 mg/kg 0.037 mg/kg 0.18 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0038 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.0091 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.011 mg/kg 0.011 mg/kg 0.011 mg/kg 0.022 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.011 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.055 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.000000112 mg/kg 2.51E‐08 mg/kg 0.000000195 mg/kg 0.000000422 mg/kg 0.00000182 mg/kg 0.00000478 mg/kg 0.00000478 mg/kg Detected N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y N N Project  Qual  Code U U U U U U U U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U J J U U Validation Note L F, F F, F F F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 4.3 No 8.60E‐03 Ecological RBSL ‐‐ No SL No SL 1.7 No 2.18E‐02 Ecological RBSL 4.3 No 8.60E‐03 Ecological RBSL 2.8 No 6.79E‐02 Ecological RBSL 5.1 No 7.25E‐03 Ecological RBSL 3.4 No 5.29E‐02 Ecological RBSL 7.29 No 1.25E‐03 Suburban Residential RBSL 53 No 1.72E‐04 Ecological RBSL 1.1 No 8.27E‐03 Ecological RBSL 0.33 No 2.76E‐02 Ecological RBSL 2.2 No 4.14E‐03 Ecological RBSL 0.387 No 2.35E‐02 Suburban Residential RBSL 0.0387 No 2.35E‐01 Suburban Residential RBSL 0.387 No 2.35E‐02 Suburban Residential RBSL 7.4 No 1.23E‐03 Ecological RBSL 0.387 No 2.35E‐02 Suburban Residential RBSL 1.2 No 3.17E‐03 Ecological RBSL 0.113 No 8.05E‐02 Suburban Residential RBSL 54 No 1.69E‐04 Ecological RBSL 0.89 No 1.02E‐02 Ecological RBSL 0.387 No 2.35E‐02 Suburban Residential RBSL 14.6 No 6.23E‐04 Suburban Residential RBSL 1.3 No 7.00E‐03 Ecological RBSL 1.2 No 7.58E‐03 Ecological RBSL 2.87 No 1.74E‐03 Suburban Residential RBSL 2460 No 2.03E‐06 Ecological RBSL 0.288 No 1.74E‐02 Suburban Residential RBSL 220 No 2.27E‐05 Ecological RBSL 0.533 No 9.38E‐03 Suburban Residential RBSL 1.89 No 2.65E‐03 Suburban Residential RBSL 6.9 No 7.25E‐04 Ecological RBSL ‐‐ No SL No SL 10 No 5.00E‐04 Ecological RBSL ‐‐ No SL No SL 3.1 No 1.61E‐03 Ecological RBSL 0.0978 No 5.11E‐02 Suburban Residential RBSL 0.104 No 4.81E‐02 Suburban Residential RBSL 130 No 3.85E‐05 Ecological RBSL 0.261 No 1.92E‐02 Suburban Residential RBSL 0.439 No 1.14E‐02 Suburban Residential RBSL 3.2 No 1.56E‐03 Ecological RBSL 23 No 2.17E‐04 Ecological RBSL ‐‐ No SL No SL 1.33 No 3.76E‐03 Suburban Residential RBSL ‐‐ No SL No SL 0.01 Yes 1.10E+00 MRL 23 No 4.78E‐04 Ecological RBSL 4.5 No 2.44E‐03 Ecological RBSL 46 No 4.78E‐04 Ecological RBSL 0.115 No 4.35E‐02 Suburban Residential RBSL 25 No 2.00E‐04 Ecological RBSL ‐‐ No SL No SL 0.195 No 2.56E‐02 Suburban Residential RBSL 23 No 2.17E‐04 Ecological RBSL 3.2 No 1.56E‐03 Ecological RBSL 0.071 No 7.04E‐02 Suburban Residential RBSL 21 No 2.38E‐04 Ecological RBSL ‐‐ No SL No SL 0.733 No 6.82E‐03 Suburban Residential RBSL 3.2 No 1.56E‐03 Ecological RBSL ‐‐ No SL No SL 9.22 No 5.42E‐04 Suburban Residential RBSL ‐‐ No SL No SL 7.28 No 6.87E‐04 Suburban Residential RBSL 22.3 No 2.24E‐04 Suburban Residential RBSL 41 No 1.22E‐04 Ecological RBSL ‐‐ No SL No SL 2.31 No 2.16E‐03 Suburban Residential RBSL 1.3 No 3.85E‐03 Ecological RBSL 8160 No 1.35E‐06 Ecological RBSL ‐‐ No SL No SL 2.97 No 1.68E‐03 Suburban Residential RBSL 3.3 No 1.52E‐03 Ecological RBSL 61 No 8.20E‐05 Ecological RBSL 73 No 6.85E‐05 Ecological RBSL 16 No 3.13E‐04 Ecological RBSL 3.4 No 1.47E‐03 Ecological RBSL 16 No 3.13E‐04 Ecological RBSL 3.7 No 1.35E‐03 Ecological RBSL 0.98 No 5.10E‐03 Ecological RBSL ‐‐ No SL No SL 210 No 2.38E‐05 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 1.1 No 4.55E‐03 Ecological RBSL 0.416 No 1.20E‐02 Suburban Residential RBSL 59 No 8.47E‐05 Ecological RBSL 85.3 No 5.86E‐05 Suburban Residential RBSL No SL No SL ‐‐ 0.797 No 6.27E‐03 Suburban Residential RBSL 170 No 2.94E‐05 Ecological RBSL 0.0204 No 2.45E‐01 Suburban Residential RBSL 0.0000057 No 1.96E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 3.46E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 37 37 37 37 190 37 180 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 9.1 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 11 11 22 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 5 5 5 5 5 5 5 5 5 5 5 5 5 55 5 5 5 5 5 5 5 5 5 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 18 18 18 18 37 18 73 3.7 3.7 3.7 1.8 1.8 3.7 3.7 3.7 3.7 3.7 1.8 3.7 3.7 3.7 3.7 3.7 3.7 3.7 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 8 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 2 1 1 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 22 1 1 1 1 1 1 1 2 1 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 4.78 4.78 4.78 4.78 ng/kg ng/kg ng/kg ng/kg 0.241 0.285 0.373 0.264 ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8270C 8270C 8270C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM Analyte 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene Phosphorus Aluminum Antimony Boron Calcium Iron Potassium Silver Sodium Tin Vanadium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Manganese Molybdenum Nickel Selenium Strontium Thallium Titanium Zinc Zirconium Mercury 1,2‐Diphenylhydrazine 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene o‐Cresol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether p‐Chloro‐m‐cresol p‐Chloroaniline 4‐Chlorophenylphenyl ether p‐Cresol p‐Nitroaniline 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Carbazole Dibenzofuran Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Diphenylamine Hexachlorobenzene Hexachlorocyclopentadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine Pentachlorophenol Phenol 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Page 3 of 108 CAS Number 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 51207319 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 121142 606202 98953 7723140 7429905 7440360 7440428 7440702 7439896 7440097 7440224 7440235 7440315 7440622 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439965 7439987 7440020 7782492 7440246 7440280 7440326 7440666 7440677 7439976 122667 95954 88062 120832 105679 51285 91587 95487 88744 88755 91941 99092 534521 101553 59507 106478 7005723 106445 100016 100027 62533 92875 65850 100516 111911 111444 108601 117817 85687 86748 132649 84662 131113 84742 117840 122394 118741 77474 67721 78591 62759 621647 87865 108952 90120 91576 83329 Result  Value 0.361 0.275 0.68 0.898 0.969 0.224 0.51 0.266 0.224 0.153 0.19 1.41 23.8 5.28 1.28 1.65 4.78 0.51 4.78 0.153 0.955 181 181 181 167 11200 1.55 0.941 2530 18800 2840 0.0941 131 0.282 37.6 3.54 104 0.573 0.276 18.2 7.39 10.8 7.13 12.9 404 0.517 13 0.322 24.8 0.307 728 44.5 2.44 0.00537 181 181 181 181 181 361 18.1 181 181 181 181 181 181 181 181 181 181 181 181 181 181 181 361 181 181 181 181 18.1 18.1 18.1 181 18.1 18.1 18.1 18.1 181 181 181 181 181 18.1 181 181 181 3.61 3.61 3.61 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00000478 mg/kg 0.00000478 mg/kg 0.00000068 mg/kg 0.00000478 mg/kg 0.000000969 mg/kg 0.00000478 mg/kg 0.00000478 mg/kg 0.00000478 mg/kg 0.00000478 mg/kg 0.000000955 mg/kg 0.000000955 mg/kg 0.00000141 mg/kg 0.0000238 mg/kg 0.00000528 mg/kg 0.00000128 mg/kg 0.00000165 mg/kg 0.00000478 mg/kg 0.00000478 mg/kg 0.00000478 mg/kg 0.000000955 mg/kg 0.000000955 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 167 mg/kg 11200 mg/kg 4.7 mg/kg 4.7 mg/kg 2530 mg/kg 18800 mg/kg 2840 mg/kg 0.47 mg/kg 23.5 mg/kg 0.941 mg/kg 37.6 mg/kg 3.54 mg/kg 104 mg/kg 0.573 mg/kg 0.276 mg/kg 18.2 mg/kg 7.39 mg/kg 10.8 mg/kg 7.13 mg/kg 12.9 mg/kg 404 mg/kg 0.195 mg/kg 13 mg/kg 0.974 mg/kg 24.8 mg/kg 0.307 mg/kg 728 mg/kg 44.5 mg/kg 2.44 mg/kg 0.00537 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.361 mg/kg 0.0181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.361 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.0181 mg/kg 0.0181 mg/kg 0.0181 mg/kg 0.181 mg/kg 0.0181 mg/kg 0.0181 mg/kg 0.0181 mg/kg 0.0181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.0181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.181 mg/kg 0.00361 mg/kg 0.00361 mg/kg 0.00361 mg/kg Detected N N Y N Y N N N N N N Y Y Y Y Y Y N Y N Y N N N Y Y N N Y Y Y N N N Y Y Y Y Y Y Y Y Y Y Y N Y N Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code U U J UJ J U U U U U U J J J J U J U J UJ UJ U J U U U U U Validation Note F *DVR, F F F, F F , F, F F, F, B F, F F, F F , F, Original Result = 0.898 F, F , Original Result = 0.241 F, F , Original Result = 0.401 Q, Q Q Q B B, F B B J J J U J U B J J J J U UJ U U U U U U U U U UJ U U UJ U UJ U UJ UJ U UJ U U UJ UJ UJ UJ U U UJ U U U U U UJ U U U U U U U UJ UJ UJ , B Q Q, Q Q Q Q, Q Q, Q Q Q, Q Q, Q Q, Q, L Q Q, Q, L Q, Q Q Q, Q Q, Q Q Q Q Q Q Q Q Q Q Q Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 37900 0.5 22 ‐‐ ‐‐ 7524 0.99 754 31 111.8 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 723 1.642 64.2 1 1210 0.761 1865 153 10.64 0.87 ‐‐ 75 7.43 ‐‐ 65 ‐‐ ‐‐ 4.3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.7 ‐‐ ‐‐ 4.3 3.4 8 ‐‐ ‐‐ 4.5 4.5 ‐‐ ‐‐ ‐‐ 0.32 90 1.5 1.2 2.3 4.5 0.11 13 ‐‐ ‐‐ 3 ‐‐ ‐‐ 0.0325 ‐‐ 2.8 5.1 7.29 53 1.1 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No No SL No SL No No No No No No No No No No No No No No No No No No No No No No No No No SL No No No SL No No SL No SL No No SL No SL No SL No SL No SL No SL No No SL No SL No No No No SL No SL No No No SL No SL No SL No No No No No No No No No SL No SL No No SL No SL No No SL No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 2.96E‐01 9.40E+00 2.14E‐01 No SL No SL 3.77E‐01 4.75E‐01 3.12E‐02 3.04E‐02 3.36E‐01 1.46E‐01 5.10E‐01 1.19E‐01 6.34E‐01 3.03E‐01 2.82E‐01 2.57E‐01 2.10E‐01 2.00E‐01 5.59E‐01 1.19E‐01 2.02E‐01 9.74E‐01 2.05E‐02 4.03E‐01 3.90E‐01 2.91E‐01 2.29E‐01 6.17E‐03 No SL 2.41E‐03 2.44E‐02 No SL 2.78E‐03 No SL No SL 4.21E‐02 No SL No SL No SL No SL No SL No SL 1.06E‐01 No SL No SL 4.21E‐02 5.32E‐02 2.26E‐02 No SL No SL 8.02E‐02 4.02E‐02 No SL No SL No SL 5.66E‐02 2.01E‐04 1.21E‐02 1.51E‐01 7.87E‐03 4.02E‐03 1.65E‐01 1.39E‐03 No SL No SL 6.03E‐02 No SL No SL 5.57E‐01 No SL 6.46E‐02 3.55E‐02 4.95E‐04 6.81E‐05 3.28E‐03 SCL Basis Background MRL Ecological RBSL Background Ecological RBSL Background Ecological RBSL Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 4.78 4.78 4.78 4.78 4.78 4.78 4.78 4.78 4.78 0.955 0.955 9.55 9.55 4.78 4.78 4.78 4.78 4.78 4.78 0.955 0.955 181 181 181 14.1 18.8 4.7 4.7 23.5 23.5 23.5 0.47 23.5 0.941 0.47 0.974 0.39 0.0974 0.195 0.585 0.195 0.195 0.39 1.95 4.87 0.195 0.39 0.974 9.74 0.39 97.4 1.95 1.95 0.0126 181 181 181 181 181 361 18.1 181 181 181 181 181 181 181 181 181 181 181 181 181 181 181 361 181 181 181 181 18.1 18.1 18.1 181 18.1 18.1 18.1 18.1 181 181 181 181 181 18.1 181 181 181 3.61 3.61 3.61 RL Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 0.361 0.275 0.382 0.357 0.384 0.224 0.51 0.266 0.224 0.153 0.19 0.751 1.06 0.285 0.241 0.361 0.264 0.51 0.177 0.153 0.19 54.2 54.2 54.2 4.7 6.4 1.55 0.941 7.52 7.52 6.02 0.0941 6.58 0.282 0.0941 0.195 0.0974 0.0195 0.0195 0.195 0.0585 0.0643 0.0974 0.39 0.974 0.0585 0.0974 0.322 1.95 0.0585 19.5 0.39 0.0974 0.00424 54.2 54.2 54.2 54.2 54.2 54.2 5.42 54.2 59.6 54.2 54.2 54.2 54.2 54.2 72.2 54.2 54.2 54.2 54.2 54.2 54.2 54.2 90.3 54.2 54.2 54.2 54.2 5.42 5.42 5.42 54.2 5.42 5.42 5.42 5.42 54.2 54.2 54.2 54.2 54.2 5.42 54.2 54.2 54.2 0.903 0.903 0.903 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Composite Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Grab Sample Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 GMBS2012 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 STBS1019 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 ELBS01 ELBS01 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP GMBS2012C001SP STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 STBS1019S001 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 RF246 RF246 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 Sample ID GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 GMBS2012C001 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 D‐3‐03 ELBS01S01 ELBS01S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 5/22/12 13:30 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 2/17/93 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons PCBs PCBs PCBs PCBs PCBs PCBs PCBs Hydrocarbons Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Metals VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 8015B 8015B 8082 8082 8082 8082 8082 8082 8082 418.1 418.1 418.1 418.1 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 7471 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 8240 9045 7060 8021A 8015M 8015M 8015M 8015M 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A Analyte Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene C12‐C14 (Kerosene Range) C21‐C30 (Lubricant Oil Range) C15‐C20 (Diesel Range) C4‐C12 (Gasoline Range) Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Hydrocarbons Chloride Fluoride Nitrate‐N Antimony Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Mercury 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene Acetone Benzene Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Ethylbenzene 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Methylene chloride Chlorobenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Arsenic Xylenes, Total C4‐C12 (Gasoline Range) C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene Page 4 of 108 CAS Number 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 EFHD (C12‐C14) EFHD (C21‐C30) EFHD (C15‐C20) GRO C4‐C12 12674112 11104282 11141165 53469219 12672296 11097691 11096825 8012951 16887006 16984488 NO3N 7440360 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7439976 71556 79345 79005 75343 75354 95501 107062 78875 541731 106467 67641 71432 75274 75252 74839 56235 75003 67663 74873 156592 10061015 124481 100414 76131 75092 108907 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 7440382 1330207 GRO C4‐C12 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) 630206 71556 79345 76131 79005 75343 75354 95636 96128 95501 107062 78875 108678 Result  Value 3.61 3.61 2.53 3.61 3.61 1.44 3.61 0.903 3.61 3.61 3.61 3.61 3.61 1.99 1.63 5.45 5.45 5.45 5.45 16.3 27.2 16.3 16.3 16.3 16.3 16.3 17 1.9 0.2 1 3.2 5.3 61 0.03 0.4 6 1.8 4.5 4.2 0.8 3 7.5 0.7 4 18 15 0.02 10 5 5 5 5 5 5 5 5 5 20 5 5 5 5 5 5 5 5 5 5 5 5 10 10 5 5 5 5 5 5 5 5 5 8.7 8 5 11 11 11 11 22 5 5 22 5 5 5 22 22 11 5 5 22 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.00361 0.00361 0.00253 0.00361 0.00361 0.00144 0.00361 0.000903 0.00361 0.00361 0.00361 0.00361 0.00361 0.00199 0.00163 5.45 5.45 5.45 5.45 0.0163 0.0272 0.0163 0.0163 0.0163 0.0163 0.0163 17 1.9 0.2 0.1 3.2 5.3 61 0.03 0.4 6 1.8 4.5 4.2 0.8 3 7.5 0.7 4 18 15 0.02 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.02 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 8.7 8 0.005 11 11 11 11 0.022 0.005 0.005 0.022 0.005 0.005 0.005 0.022 0.022 0.011 0.005 0.005 0.022 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N Y N N Y N Y N N N N N Y Y N N N N N N N N N N N Y Y Y N N N Y N N Y Y Y N N Y N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N N N N N N N N N N N N N N N N N N Project  Qual  Code UJ U J U U J U J UJ U U UJ UJ J J U U U U U U U U U U U Validation Note Q Q Q, Q Q Q Q, Q Q, Q Q U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U UJ UJ UJ UJ U U U U U U U U U U U U U H S, See Report Section 7 S, See Report Section 7 S, See Report Section 7 S, See Report Section 7 Boeing Soil Char Level  (mg/kg) 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 1400 1400 1400 1 0.12 0.18 0.082 0.043 0.017 0.039 0.025 ‐‐ ‐‐ 35 2340 0.5 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 1.642 64.2 1 0.99 0.761 111.8 153 0.87 2460 0.288 0.533 1.89 6.9 130 0.261 0.439 23 1.33 46 0.115 0.195 23 3.2 0.071 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 2.31 220 2.97 21 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ 24.2 3.4 1 ‐‐ ‐‐ ‐‐ 2.87 2460 0.288 220 0.533 1.89 6.9 3.1 0.0978 130 0.261 0.439 3.2 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No Yes No No No No No No No No SL No SL No No Yes No No No No No No No No No No Yes No Yes No No No No No No No No No No No No No No No No No No No No SL No No No No SL No No No No No No No No No SL No No No No No SL No No Yes No SL No SL No SL No No No No No No No No No No No No No Ratio Boeing Soil Char Level 1.09E‐02 1.64E‐03 6.54E‐03 9.33E‐02 9.33E‐03 1.95E‐04 9.33E‐03 7.53E‐04 3.19E‐02 6.69E‐05 4.06E‐03 9.33E‐03 2.47E‐04 1.53E‐03 1.36E‐03 3.89E‐03 3.89E‐03 3.89E‐03 5.45E+00 1.36E‐01 1.51E‐01 1.99E‐01 3.79E‐01 9.59E‐01 4.18E‐01 6.52E‐01 No SL No SL 5.71E‐03 4.27E‐05 6.40E+00 2.19E‐01 2.99E‐01 6.25E‐03 9.20E‐01 9.98E‐02 6.88E‐02 1.07E‐01 1.24E‐01 4.87E‐01 4.67E‐02 7.50E+00 7.07E‐01 5.26E+00 1.61E‐01 9.80E‐02 2.30E‐02 4.07E‐06 1.74E‐02 9.38E‐03 2.65E‐03 7.25E‐04 3.85E‐05 1.92E‐02 1.14E‐02 2.17E‐04 3.76E‐03 4.35E‐04 4.35E‐02 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 No SL 6.82E‐03 1.56E‐03 5.42E‐04 No SL 6.87E‐04 2.16E‐03 4.55E‐05 3.37E‐03 2.38E‐04 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 1.47E‐03 No SL 3.31E‐01 1.47E‐03 1.10E+01 No SL No SL No SL 7.67E‐03 2.03E‐06 1.74E‐02 1.00E‐04 9.38E‐03 2.65E‐03 7.25E‐04 7.10E‐03 2.25E‐01 8.46E‐05 1.92E‐02 1.14E‐02 6.88E‐03 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Background Background Ecological RBSL Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 3.61 ug/kg 5.45 mg/kg 5.45 mg/kg 5.45 mg/kg 5.45 mg/kg 16.3 ug/kg 27.2 ug/kg 16.3 ug/kg 16.3 ug/kg 16.3 ug/kg 16.3 ug/kg 16.3 ug/kg 10 mg/kg 0.1 mg/kg 0.1 mg/kg 0.1 mg/kg 3.2 mg/kg 5.3 mg/kg 0.2 mg/kg 0.03 mg/kg 0.4 mg/kg 0.7 mg/kg 0.7 mg/kg 0.6 mg/kg 4.2 mg/kg 0.8 mg/kg 1.5 mg/kg 7.5 mg/kg 0.7 mg/kg 4 mg/kg 0.8 mg/kg 0.2 mg/kg 0.02 mg/kg 10 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 20 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 10 ug/kg 10 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 0.100000001 pH Units 5 mg/kg 5 ug/kg 11 mg/kg 11 mg/kg 11 mg/kg 11 mg/kg 22 ug/kg 5 ug/kg 5 ug/kg 22 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 22 ug/kg 22 ug/kg 11 ug/kg 5 ug/kg 5 ug/kg 22 ug/kg MDL 0.903 0.903 0.903 0.903 0.903 0.903 0.903 0.903 0.903 0.903 0.903 0.903 0.542 0.903 0.903 1.09 1.09 1.09 1.09 3.02 8.74 2.18 5.08 5.08 2.83 2.83 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1 mg/kg 3.2 mg/kg 5.3 mg/kg 0.03 mg/kg 0.4 mg/kg 4.2 mg/kg 0.8 mg/kg 7.5 mg/kg 0.7 mg/kg 4 mg/kg 0.02 10 5 5 5 5 5 5 5 5 5 20 5 5 5 5 5 5 5 5 5 5 5 5 10 10 5 5 5 5 5 5 5 5 5 mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5 11 11 11 11 22 5 5 22 5 5 5 22 22 11 5 5 22 ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS03 ELBS03 ELBS03 ELBS03 ELBS04 ELBS04 ELBS05 ELBS05 ELBS05 ELBS06 ELBS07 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD247 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RD248 RF247 RF247 RF248 RF248 RS691 RD976 RD976 RD976 RD976 RS504 RS504 RS505 RS505 RS647 RS645 RS646 RS887 RS887 RS887 RS887 RS887 RS887 RS887 Sample ID ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S01 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S02 ELBS02S01 ELBS02S01 ELBS02S02 ELBS02S02 ELBS02S01 ELBS03S01 ELBS03S01 ELBS03S01 ELBS03S01 ELBS04S01 ELBS04S01 ELBS05S01 ELBS05S01 ELBS05S02 ELBS06S01 ELBS07S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 11/11/97 0:00 1/29/98 0:00 12/2/97 0:00 12/2/97 0:00 12/2/97 0:00 12/2/97 0:00 12/5/97 0:00 12/5/97 0:00 12/5/97 0:00 12/5/97 0:00 1/23/98 0:00 1/23/98 0:00 1/23/98 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 4 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 4 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Metals Inorganics Metals Metals Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Metals Inorganics Metals Metals Metals Metals Inorganics Metals Metals Metals Metals Metals Metals Analysis  Method 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8015M 8015M 8015M 8015M 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 8021A 9045 7060 9045 7060 7196 8015M 8015M 8015M 8015M 9045 7060 9045 7060 7060 7060 7060 9045 6010 6010 6010 6010 6010 6010 Analyte 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene Methyl ethyl ketone 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether Acetone Benzene Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C4‐C12 (Gasoline Range) C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene Methyl ethyl ketone 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether Acetone Benzene Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride pH Arsenic pH Arsenic Hexavalent Chromium C4‐C12 (Gasoline Range) C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) pH Arsenic pH Arsenic Arsenic Arsenic Arsenic pH Aluminum Antimony Barium Beryllium Boron Cadmium Page 5 of 108 CAS Number 541731 106467 78933 75887 110758 67641 71432 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 75718 100414 179601231 75092 95476 127184 108883 156605 10061026 79016 75694 75014 1330207 GRO C4‐C12 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) 630206 71556 79345 76131 79005 75343 75354 95636 96128 95501 107062 78875 108678 541731 106467 78933 75887 110758 67641 71432 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 75718 100414 179601231 75092 95476 127184 108883 156605 10061026 79016 75694 75014 E‐10139 7440382 E‐10139 7440382 18540299 GRO C4‐C12 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) E‐10139 7440382 E‐10139 7440382 7440382 7440382 7440382 E‐10139 7429905 7440360 7440393 7440417 7440428 7440439 Result  Value 11 11 54 22 54 54 5 5 10 11 5 5 11 10 11 22 5 5 11 5 5 22 5 5 5 5 5 5 5 11 6 11 11 11 11 22 6 6 22 6 6 6 22 22 11 6 6 22 11 11 56 22 56 56 6 6 12 11 6 6 11 12 11 22 6 6 11 6 6 22 6 6 6 6 6 6 6 11 7.9 61 8.2 6 5 12 12 12 12 7.6 6 7.4 110 6 7 7 8.1 7400 10 100 1 10 1 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 0.011 0.011 0.054 0.022 0.054 0.054 0.005 0.005 0.01 0.011 0.005 0.005 0.011 0.01 0.011 0.022 0.005 0.005 0.011 0.005 0.005 0.022 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.011 0.006 11 11 11 11 0.022 0.006 0.006 0.022 0.006 0.006 0.006 0.022 0.022 0.011 0.006 0.006 0.022 0.011 0.011 0.056 0.022 0.056 0.056 0.006 0.006 0.012 0.011 0.006 0.006 0.011 0.012 0.011 0.022 0.006 0.006 0.011 0.006 0.006 0.022 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.011 7.9 61 8.2 6 5 12 12 12 12 7.6 6 7.4 110 6 7 7 8.1 7400 10 100 1 10 1 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y N N N N N Y N Y Y N Y Y Y Y N Y N N N Project  Qual  Code Validation Note U U U U U U U U UJ U U U U UJ U U U U U U U U U U U U U U U U U UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U UJ U U U U UJ U U U U U U U U U U U U U U U U J H J H U UJ UJ UJ UJ J U J J U See Report Section 99 See Report Section 99 S, See Report Section 7 S, See Report Section 7 S, See Report Section 7 S, See Report Section 7 See Report Section 99 See Report Section 99 S, See Report Section 7 S, See Report Section 7 S, See Report Section 7 S, See Report Section 7 H H Q J H UJ Q U U UJ Q Boeing Soil Char Level  (mg/kg) 23 1.33 8160 ‐‐ 0.01 46 0.115 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 41 2.31 3.3 2.97 3.4 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1 ‐‐ ‐‐ ‐‐ 2.87 2460 0.288 220 0.533 1.89 6.9 3.1 0.0978 130 0.261 0.439 3.2 23 1.33 8160 ‐‐ 0.01 46 0.115 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 41 2.31 3.3 2.97 3.4 0.416 59 85.3 ‐‐ 0.797 170 0.0204 ‐‐ 24.2 ‐‐ 24.2 1.29 1 ‐‐ ‐‐ ‐‐ ‐‐ 24.2 ‐‐ 24.2 24.2 24.2 24.2 ‐‐ 37900 0.5 203.8 4.8 22 0.435 Exceeds Boeing Soil Char Level No No No No SL Yes No No No No No No No No SL No No No SL No No SL No No No No No No No No No SL No No No No Yes No SL No SL No SL No No No No No No No No No No No No No No No No No SL Yes No No No No No No No No SL No No No SL No No SL No No No No No No No No No SL No No No No SL Yes No SL No Yes Yes No SL No SL No SL No SL No No SL Yes No No No No SL No Yes No No No Yes Ratio Boeing Soil Char Level 4.78E‐04 8.27E‐03 6.62E‐06 No SL 5.40E+00 1.17E‐03 4.35E‐02 2.56E‐02 4.35E‐04 3.44E‐03 7.04E‐02 2.38E‐04 No SL 1.36E‐02 3.44E‐03 No SL 5.42E‐04 No SL 2.68E‐04 2.16E‐03 1.52E‐03 7.41E‐03 1.47E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 5.39E‐01 1.76E‐03 1.10E+01 No SL No SL No SL 7.67E‐03 2.44E‐06 2.08E‐02 1.00E‐04 1.13E‐02 3.17E‐03 8.70E‐04 7.10E‐03 2.25E‐01 8.46E‐05 2.30E‐02 1.37E‐02 6.88E‐03 4.78E‐04 8.27E‐03 6.86E‐06 No SL 5.60E+00 1.22E‐03 5.22E‐02 3.08E‐02 5.22E‐04 3.44E‐03 8.45E‐02 2.86E‐04 No SL 1.64E‐02 3.44E‐03 No SL 6.51E‐04 No SL 2.68E‐04 2.60E‐03 1.82E‐03 7.41E‐03 1.76E‐03 1.44E‐02 1.02E‐04 7.03E‐05 No SL 7.53E‐03 3.53E‐05 5.39E‐01 No SL 2.52E+00 No SL 2.48E‐01 3.88E+00 1.20E+01 No SL No SL No SL No SL 2.48E‐01 No SL 4.55E+00 2.48E‐01 2.89E‐01 2.89E‐01 No SL 1.95E‐01 2.00E+01 4.91E‐01 2.08E‐01 4.55E‐01 2.30E+00 SCL Basis Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Background Background Suburban Residential RBSL Background Background Background Background Background Background MRL Background Ecological RBSL Ecological RBSL Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 11 ug/kg 11 ug/kg 54 ug/kg 22 ug/kg 54 ug/kg 54 ug/kg 5 ug/kg 5 ug/kg 10 ug/kg 11 ug/kg 5 ug/kg 5 ug/kg 11 ug/kg 10 ug/kg 11 ug/kg 22 ug/kg 5 ug/kg 5 ug/kg 11 ug/kg 5 ug/kg 5 ug/kg 22 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 5 ug/kg 11 ug/kg 6 ug/kg 11 mg/kg 11 mg/kg 11 mg/kg 11 mg/kg 22 ug/kg 6 ug/kg 6 ug/kg 22 ug/kg 6 ug/kg 6 ug/kg 6 ug/kg 22 ug/kg 22 ug/kg 11 ug/kg 6 ug/kg 6 ug/kg 22 ug/kg 11 ug/kg 11 ug/kg 56 ug/kg 22 ug/kg 56 ug/kg 56 ug/kg 6 ug/kg 6 ug/kg 12 ug/kg 11 ug/kg 6 ug/kg 6 ug/kg 11 ug/kg 12 ug/kg 11 ug/kg 22 ug/kg 6 ug/kg 6 ug/kg 11 ug/kg 6 ug/kg 6 ug/kg 22 ug/kg 6 ug/kg 6 ug/kg 6 ug/kg 6 ug/kg 6 ug/kg 6 ug/kg 6 ug/kg 11 ug/kg 0.100000001 pH Units 5 mg/kg 0.100000001 pH Units 5 mg/kg 5 mg/kg 12 mg/kg 12 mg/kg 12 mg/kg 12 mg/kg 0.100000001 pH Units 6 mg/kg 0.100000001 pH Units 6 mg/kg 6 mg/kg 6 mg/kg 6 mg/kg 10 10 1 1 10 1 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL  Units MDL 11 11 54 22 54 54 5 5 10 11 5 5 11 10 11 22 5 5 11 5 5 22 5 5 5 5 5 5 5 11 6 11 11 11 11 22 6 6 22 6 6 6 22 22 11 6 6 22 11 11 56 22 56 56 6 6 12 11 6 6 11 12 11 22 6 6 11 6 6 22 6 6 6 6 6 6 6 11 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5 12 12 12 12 mg/kg mg/kg mg/kg mg/kg mg/kg 6 mg/kg 6 mg/kg 10 mg/kg 1 mg/kg 10 mg/kg 1 mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 9/22/99 0:00 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 13:20 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/8/08 10:30 4/10/08 13:34 4/10/08 13:34 4/10/08 13:34 4/10/08 13:34 4/10/08 13:34 4/10/08 10:36 4/10/08 10:36 4/10/08 10:36 4/10/08 10:36 4/10/08 10:36 4/8/08 9:50 4/8/08 9:50 4/8/08 9:50 4/8/08 9:50 4/8/08 9:50 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Chloride Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium 16887006 16984488 NO3N NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS10 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1003 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1004 ELBS1005 ELBS1005 ELBS1005 ELBS1005 ELBS1005 ELBS1006 ELBS1006 ELBS1006 ELBS1006 ELBS1006 ELBS1007 ELBS1007 ELBS1007 ELBS1007 ELBS1007 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 RS887 RS887 RS887 RS887 RS887 RS887 RS887 RS887 RS887 RS887 RS887 RS887 RS887 ELBS1003S010 ELBS1003S010 ELBS1003S010 ELBS1003S010 ELBS1003S010 ELBS1003X010 ELBS1003X010 ELBS1003X010 ELBS1003X010 ELBS1003X010 ELBS1004D010 ELBS1004D010 ELBS1004D010 ELBS1004D010 ELBS1004D010 ELBS1004S010 ELBS1004S010 ELBS1004S010 ELBS1004S010 ELBS1004S010 ELBS1005S010 ELBS1005S010 ELBS1005S010 ELBS1005S010 ELBS1005S010 ELBS1006S010 ELBS1006S010 ELBS1006S010 ELBS1006S010 ELBS1006S010 ELBS1007S010 ELBS1007S010 ELBS1007S010 ELBS1007S010 ELBS1007S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Sample ID ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS10S01 ELBS1003S010 ELBS1003S010 ELBS1003S010 ELBS1003S010 ELBS1003S010 ELBS1004S010 ELBS1004S010 ELBS1004S010 ELBS1004S010 ELBS1004S010 Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics 6010 6010 6010 6010 6010 6010 6010 6010 6010 7060 7471 7740 7841 8015B 8015B 8015B 8015B 9045C 8015B 8015B 8015B 8015B 9045C 8015B 8015B 8015B 8015B 9045C 8015B 8015B 8015B 8015B 9045C 8015B 8015B 8015B 8015B 9045C 8015B 8015B 8015B 8015B 9045C 8015B 8015B 8015B 8015B 9045C 8260B 8015B 8015B 8015B 8015B 9045C 9056 Chromium Cobalt Copper Lead Molybdenum Nickel Silver Vanadium Zinc Arsenic Mercury Selenium Thallium C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH Bromide 7440473 7440484 7440508 7439921 7439987 7440020 7440224 7440622 7440666 7440382 7439976 7782492 7440280 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 24959679 Page 6 of 108 Result  Value 11 11 6 5 10 14 1 29 88 5 0.2 5 5 3.53 3.53 3.53 3.53 8.13 13 13 13 13 7.68 3.97 3.97 3.97 3.97 7.63 3.88 3.88 3.88 3.88 7.09 3.85 3.85 3.85 3.85 7.86 3.75 3.75 3.75 3.75 8.28 3.91 3.91 3.91 3.91 6.96 1.8 4.9 4.9 4.9 1.2 8.5 0.4 Result  Value  Units Result  in SL Units SL Units Detected Project  Qual  Code mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg 11 11 6 5 10 14 1 29 88 5 0.2 5 5 3.53 3.53 3.53 3.53 8.13 13 13 13 13 7.68 3.97 3.97 3.97 3.97 7.63 3.88 3.88 3.88 3.88 7.09 3.85 3.85 3.85 3.85 7.86 3.75 3.75 3.75 3.75 8.28 3.91 3.91 3.91 3.91 6.96 0.0018 4.9 4.9 4.9 1.2 8.5 5.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg Y Y Y N N Y N Y Y N N N N N N N N Y N N N N Y N N N N Y N N N N Y N N N N Y N N N N Y N N N N Y N N N N Y Y N 5.2 0.86 0.78 0.52 0.89 3 10000 81 0.68 1 12 4.1 10 2200 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.2 5.2 0.78 0.52 0.89 3 10000 81 0.68 5.2 12 4.1 10 2200 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y Y Y Y Y Y Y N Y Y Y Y U U J J J J 130 32 31 1.6 0.56 3.5 0.052 7 3.5 0.27 6.7 0.11 0.036 0.12 0.021 4.5 4.5 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 130 32 31 1.6 0.56 3.5 0.052 7 3.5 0.27 6.7 0.11 0.036 0.12 0.021 0.0045 0.0045 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N J J J J J J UJ UJ 21 1.2 21 21 1.1 21 21 21 21 21 21 21 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.021 0.0012 0.021 0.021 0.0011 0.021 0.021 0.021 0.021 0.021 0.021 0.021 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y N N Y N N N N N N N U J U U J U U U U U U U J J UJ U J U J U U UJ U U U U U Validation Note Q Q Q Q E,Q Q U U U U U U U U U U U U U U U U U U U U U U U U U U U U J $ $ $ U J B, result changed from 4.4 and  MDL from 2 H H H A U J A J A U J F, RL changed from 120 and  MDL from 61 A J J J J Q,A Q Q Q $,H $,H B,$, result changed from 6.8 B,$, result changed from 1 $ $ $ $ $ $ $ $ Boeing Soil Char Level  (mg/kg) 60.11 26.18 42 33.9 1.642 64.2 0.99 111.8 153 24.2 0.87 1 0.761 1400 1400 1400 1 ‐‐ 1400 1400 1400 1 ‐‐ 1400 1400 1400 1 ‐‐ 1400 1400 1400 1 ‐‐ 1400 1400 1400 1 ‐‐ 1400 1400 1400 1 ‐‐ 1400 1400 1400 1 ‐‐ 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No No No Yes No Yes No No No No Yes Yes No No No Yes No SL No No No Yes No SL No No No Yes No SL No No No Yes No SL No No No Yes No SL No No No Yes No SL No No No Yes No SL No No No No Yes No SL No SL Ratio Boeing Soil Char Level 1.83E‐01 4.20E‐01 1.43E‐01 1.47E‐01 6.09E+00 2.18E‐01 1.01E+00 2.59E‐01 5.75E‐01 2.07E‐01 2.30E‐01 5.00E+00 6.57E+00 2.52E‐03 2.52E‐03 2.52E‐03 3.53E+00 No SL 9.29E‐03 9.29E‐03 9.29E‐03 1.30E+01 No SL 2.84E‐03 2.84E‐03 2.84E‐03 3.97E+00 No SL 2.77E‐03 2.77E‐03 2.77E‐03 3.88E+00 No SL 2.75E‐03 2.75E‐03 2.75E‐03 3.85E+00 No SL 2.68E‐03 2.68E‐03 2.68E‐03 3.75E+00 No SL 2.79E‐03 2.79E‐03 2.79E‐03 3.91E+00 No SL 5.29E‐04 3.50E‐03 3.50E‐03 3.50E‐03 1.20E+00 No SL No SL ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 No SL No No No SL No No SL No No No No No No No No No SL 1.49E‐01 3.33E‐04 No SL 1.03E‐03 No SL 2.64E‐01 3.97E‐01 1.42E‐01 2.36E‐01 2.00E‐01 1.57E‐01 1.55E‐01 2.92E‐01 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 No No No No Yes No No No No No No No No No No No No 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 No No No No No No No No No No No No SCL Basis Background Background Background Background Background Background Ecological RBSL Background Background Background Ecological RBSL MRL Suburban Residential RBSL SCL Units RL RL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg 2 2 2 5 10 5 1 2 1 5 0.2 5 5 3.53 3.53 3.53 3.53 0.1 13 13 13 13 0.01 3.97 3.97 3.97 3.97 0.1 3.88 3.88 3.88 3.88 0.1 3.85 3.85 3.85 3.85 0.1 3.75 3.75 3.75 3.75 0.1 3.91 3.91 3.91 3.91 0.1 1.8 4.9 4.9 4.9 4.9 0.1 5.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg Background Background Ecological RBSL Ecological RBSL Background Background Background Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.2 5.2 5.2 5.2 5.2 5.2 10 0.52 0.31 5.2 1 0.52 6.6 100 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.72E‐01 2.86E‐01 2.03E‐01 1.50E‐01 1.12E+00 1.45E‐01 1.20E‐01 1.67E‐01 1.03E‐01 1.64E‐01 1.04E‐01 1.10E‐01 3.64E‐02 1.58E‐01 2.41E‐02 4.50E‐04 2.05E‐01 Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 130 1 5.2 26 1 0.52 0.21 0.21 0.42 0.1 0.42 1 0.21 0.21 0.031 4.5 4.5 6.56E‐02 1.33E‐05 9.13E‐03 4.67E‐03 1.00E‐02 1.62E‐03 6.46E‐01 2.88E‐03 3.96E‐04 1.91E‐02 6.36E‐02 9.55E‐03 Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 21 21 21 21 21 21 21 21 21 21 21 21 Ecological RBSL Ecological RBSL Ecological RBSL Background MDL  Units MDL Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y mg/kg Y mg/kg Y Y mg/kg Y Y Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y pH Units Y mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg pH Units Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y pH Units mg/kg Y mg/kg Y mg/kg Y mg/kg Y pH Units Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y pH Units Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y pH Units Y ug/kg Y mg/kg Y mg/kg Y mg/kg Y mg/kg Y Y mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 5.2 0.86 0.33 0.35 0.52 1.8 5.1 0.25 0.16 1 0.42 0.1 0.31 43 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 130 0.64 1 0.71 0.013 0.015 0.0064 0.084 0.052 0.017 0.042 0.083 0.0046 0.0031 0.0058 0.39 0.52 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.5 0.17 0.31 0.49 0.9 0.33 0.48 0.27 0.32 0.17 0.18 0.14 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 5 10 1 5 0.2 5 5 1.17 1.17 1.17 1.17 0.01 4.3 4.3 4.3 4.3 0.01 1.31 1.31 1.31 1.31 0.01 1.28 1.28 1.28 1.28 0.01 1.27 1.27 1.27 1.27 0.01 1.24 1.24 1.24 1.24 0.01 1.29 1.29 1.29 1.29 0.01 1.2 0.98 0.98 0.98 0.99 0.4 Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S010 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:00 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 EEL EEL CC 1 Soil Boring ELBS1011 ELBS1011S060 Primary Sample 3/26/08 9:10 Soil 5 EEL EEL EEL CC 1 EEL CC 1 Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011S060 ELBS1011S060 Primary Sample Primary Sample 3/26/08 9:10 Soil 3/26/08 9:10 Soil EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Project  Qual  Code mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N U U U U U U U U U U U U U UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U U U J J U 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 9056 Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 6 In Place Primary Result Inorganics 9056 Chloride 16887006 5.7 mg/kg 5.7 mg/kg N U 5 5 6 In Place 6 In Place Primary Result Primary Result Inorganics Inorganics 9056 9056 Fluoride Nitrate‐N 16984488 NO3N 5.7 mg/kg 0.86 mg/kg 5.7 mg/kg 0.86 mg/kg N Y U J 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 N N Y Y Y Y Y Y Y Y Y U UJ J Page 7 of 108 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.00089 0.0018 0.0018 0.0045 0.0018 0.0018 0.0045 0.0018 0.0045 0.00089 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.045 0.0089 0.0045 0.014 0.0018 0.0045 0.0045 0.0018 0.0045 0.0045 0.00089 0.0018 0.0045 0.0018 0.0045 0.0045 0.0018 0.0018 0.0018 0.0018 0.00089 0.0045 0.0018 0.0089 0.0045 0.0045 0.0018 0.0045 0.0018 0.0045 0.0018 0.0045 0.0018 0.0045 0.00089 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.0018 0.0019 5.4 5.4 4.1 1.4 5.7 Detected SL Units PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics 5.7 0.57 5 19000 100 1.1 1.3 21 5.8 23 1600 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place 21 21 21 21 21 21 21 21 21 21 21 21 21 0.89 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 8.9 4.5 14 1.8 4.5 4.5 1.8 4.5 4.5 0.89 1.8 4.5 1.8 4.5 4.5 1.8 1.8 1.8 1.8 0.89 4.5 1.8 8.9 4.5 4.5 1.8 4.5 1.8 4.5 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 1.9 5.4 5.4 4.1 1.4 0.44 Result  Value  Units 5.7 5.7 5 19000 100 1.1 1.3 21 5.8 23 1600 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg J Validation Note $ $ $ $ $ $ $ $ $ $ $ $ $ $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H B,$,H, RL changed from 8.9 $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $ $ B, result changed from 4.9 and  MDL from 2.2 F, result changed from 2.3 and  MDL from 0.93 H F, result changed from 0.55  and MDL from 0.38 H A J J A J A Boeing Soil Char Level  (mg/kg) 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No No No Yes No SL ‐‐ No SL 35 2340 No No ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 No SL No No SL No No No No No No No No Ratio Boeing Soil Char Level 5.43E‐02 5.43E‐01 5.43E‐02 2.84E‐03 5.43E‐02 1.75E‐02 1.86E‐01 3.89E‐04 2.36E‐02 5.43E‐02 1.44E‐03 1.62E‐02 1.75E‐02 3.10E‐04 7.32E‐07 6.25E‐03 2.05E‐05 3.38E‐03 9.52E‐04 6.52E‐04 No SL 4.50E‐04 No SL 5.81E‐04 4.60E‐02 1.73E‐02 1.38E‐05 6.90E‐03 4.10E‐03 5.63E‐04 7.83E‐05 No SL 1.35E‐03 No SL 4.50E+00 3.87E‐04 1.00E‐03 3.04E‐04 1.57E‐02 1.80E‐04 No SL 9.23E‐03 1.96E‐04 1.41E‐03 1.25E‐02 8.57E‐05 No SL 2.46E‐03 1.41E‐03 No SL 1.95E‐04 No SL 1.38E‐03 2.47E‐04 3.99E‐05 1.10E‐04 7.79E‐04 1.09E‐06 No SL 1.52E‐03 5.45E‐04 7.38E‐05 2.47E‐05 2.81E‐04 5.29E‐04 2.81E‐04 4.86E‐04 4.59E‐03 No SL 8.57E‐06 4.09E‐03 4.33E‐03 3.05E‐05 2.11E‐05 No SL 2.26E‐03 2.65E‐05 8.82E‐02 5.59E‐04 3.86E‐03 3.86E‐03 2.93E‐03 1.40E+00 No SL SCL Basis Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 21 21 21 21 21 21 21 21 21 21 21 21 21 0.89 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 8.9 4.5 14 1.8 4.5 4.5 1.8 4.5 4.5 0.89 1.8 4.5 1.8 4.5 4.5 1.8 1.8 1.8 1.8 0.89 4.5 1.8 8.9 4.5 4.5 1.8 4.5 1.8 4.5 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 1.9 5.4 5.4 5.4 5.4 5.7 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL 0.15 0.15 0.15 0.21 0.14 0.2 0.25 0.22 0.24 0.25 0.34 0.32 0.18 0.64 0.49 0.62 0.4 0.81 0.52 0.62 0.54 0.5 0.69 0.57 0.52 0.53 0.5 0.63 0.54 0.56 0.57 0.53 0.64 0.55 4.5 1.6 0.94 3.4 0.48 0.55 0.55 0.48 0.48 0.49 0.45 0.6 0.63 0.57 0.39 0.78 0.59 0.25 0.58 0.63 0.41 0.33 0.72 1.7 1.1 0.79 1.2 0.54 0.46 0.55 0.67 0.71 0.48 0.47 0.4 0.6 0.51 0.72 0.64 0.39 0.42 0.54 0.43 0.28 1.2 1.1 1.1 1.1 1.1 0.44 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg 5.7 mg/kg 5.7 mg/kg Y Y Y 1.63E‐01 Ecological RBSL 3.68E‐04 Ecological RBSL mg/kg mg/kg 5.7 mg/kg 5.7 mg/kg 5.7 mg/kg 0.36 mg/kg Y Y Y Y Y Y No SL 6.60E‐03 No SL 5.01E‐01 4.91E‐01 2.29E‐01 5.91E‐02 3.49E‐01 2.22E‐01 3.57E‐01 2.13E‐01 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.7 0.57 2 5.6 0.27 0.17 1.1 0.45 0.11 0.34 46 Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background 5.7 5.7 5.7 11 0.57 0.34 5.7 1.1 0.57 7.1 110 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Sample  Bottom  Remediation  Depth Status (feet bgs) Result Type Analytical Class Analysis  Method Analyte CAS Number EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene Page 8 of 108 Result  Value Result  Value  Units Result  in SL Units SL Units Detected Project  Qual  Code 140 41 43 2.9 0.34 4.9 0.057 7.9 5 0.24 13 0.26 0.093 0.21 0.0098 4.8 4.8 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 140 41 43 2.9 0.34 4.9 0.057 7.9 5 0.24 13 0.26 0.093 0.21 0.0098 0.0048 0.0048 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N U J J J J J J J UJ UJ 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 22 1.3 22 22 1.4 22 22 22 22 22 22 22 0.25 0.28 0.61 0.72 1 22 22 22 22 22 22 0.24 0.96 1.9 1.9 4.8 1.9 1.9 4.8 1.9 4.8 0.96 1.9 4.8 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.8 48 9.6 4.8 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.022 0.0013 0.022 0.022 0.0014 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.00025 0.00028 0.00061 0.00072 0.001 0.022 0.022 0.022 0.022 0.022 0.022 0.00024 0.00096 0.0019 0.0019 0.0048 0.0019 0.0019 0.0048 0.0019 0.0048 0.00096 0.0019 0.0048 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0048 0.048 0.0096 0.0048 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y N N Y N N N N N N N Y Y Y Y Y N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N U J U U J U U U U U U U J J J J J U U U U U U J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 9.6 1.9 4.8 4.8 1.9 4.8 4.8 0.96 1.9 4.8 1.9 4.8 4.8 1.9 1.9 1.9 1.9 0.96 4.8 1.9 9.6 4.8 4.8 1.9 4.8 1.9 4.8 1.9 4.8 1.9 4.8 0.96 1.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0096 0.0019 0.0048 0.0048 0.0019 0.0048 0.0048 0.00096 0.0019 0.0048 0.0019 0.0048 0.0048 0.0019 0.0019 0.0019 0.0019 0.00096 0.0048 0.0019 0.0096 0.0048 0.0048 0.0019 0.0048 0.0019 0.0048 0.0019 0.0048 0.0019 0.0048 0.00096 0.0019 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ J J J J Validation Note F, result changed from 100  and MDL from 67 A A,Q Q Q Q $,H $,H B,$, result changed from 7.9 B,$, result changed from 1 $ $ $ $ $ $ $ $ *III $ $ $ $ $ $ $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H B,$,H, Result changed from  4.6 $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Boeing Soil Char Level  (mg/kg) Ratio Exceeds Boeing Boeing Soil Char Soil Char Level Level SCL Basis SCL Units RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 No No No No No No No No No No No No No No No No No 1.86E‐01 3.67E‐01 2.81E‐01 2.73E‐01 6.80E‐01 2.02E‐01 1.31E‐01 1.88E‐01 1.47E‐01 1.46E‐01 2.02E‐01 2.60E‐01 9.39E‐02 2.76E‐01 1.13E‐02 4.80E‐04 2.18E‐01 Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 140 1.1 5.7 28 1.1 0.57 0.23 0.23 0.45 0.11 0.45 1.1 0.23 0.23 0.034 4.8 4.8 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 140 0.7 1.1 0.77 0.014 0.017 0.0069 0.092 0.057 0.018 0.045 0.091 0.005 0.0034 0.0063 0.42 0.56 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No 6.88E‐02 1.44E‐05 9.57E‐03 4.89E‐03 1.27E‐02 1.69E‐03 6.77E‐01 3.02E‐03 4.15E‐04 2.00E‐02 6.67E‐02 1.00E‐02 6.46E‐04 7.24E‐03 1.58E‐03 9.73E‐05 8.33E‐04 1.95E‐01 4.07E‐04 2.47E‐02 5.68E‐02 1.51E‐03 1.69E‐02 2.00E‐04 3.34E‐04 7.72E‐07 6.60E‐03 2.18E‐05 3.56E‐03 1.01E‐03 6.96E‐04 No SL 4.80E‐04 No SL 6.13E‐04 4.91E‐02 1.83E‐02 1.46E‐05 7.28E‐03 4.33E‐03 5.94E‐04 8.26E‐05 No SL 1.43E‐03 No SL 4.80E+00 4.17E‐04 1.07E‐03 Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 0.96 1.9 1.9 4.8 1.9 1.9 4.8 1.9 4.8 0.96 1.9 4.8 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.8 48 9.6 4.8 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.7 0.18 0.33 0.52 0.96 0.36 0.51 0.29 0.34 0.18 0.19 0.15 0.16 0.16 0.16 0.22 0.21 0.27 0.23 0.25 0.27 0.36 0.35 0.2 0.68 0.53 0.67 0.43 0.87 0.56 0.67 0.58 0.54 0.74 0.62 0.56 0.57 0.54 0.67 0.58 0.61 0.62 0.57 0.68 0.6 4.8 1.7 1 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No 2.09E‐04 1.65E‐02 1.92E‐04 No SL 9.74E‐03 2.09E‐04 1.50E‐03 1.35E‐02 9.05E‐05 No SL 2.59E‐03 1.50E‐03 No SL 2.06E‐04 No SL 1.46E‐03 2.61E‐04 4.30E‐05 1.17E‐04 8.23E‐04 1.18E‐06 No SL 1.62E‐03 5.76E‐04 7.87E‐05 2.60E‐05 3.00E‐04 5.59E‐04 3.00E‐04 5.14E‐04 4.90E‐03 No SL 9.05E‐06 Ecological RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 9.6 1.9 4.8 4.8 1.9 4.8 4.8 0.96 1.9 4.8 1.9 4.8 4.8 1.9 1.9 1.9 1.9 0.96 4.8 1.9 9.6 4.8 4.8 1.9 4.8 1.9 4.8 1.9 4.8 1.9 4.8 0.96 1.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.7 0.52 0.59 0.6 0.52 0.52 0.53 0.48 0.65 0.67 0.62 0.42 0.84 0.64 0.27 0.63 0.67 0.44 0.36 0.78 1.9 1.2 0.85 1.2 0.58 0.49 0.59 0.72 0.76 0.52 0.5 0.43 0.65 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1011 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1011S060 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 9:10 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 EEL EEL CC 1 Soil Boring ELBS1012 ELBS1012S010 Primary Sample 3/26/08 10:30 Soil 0.5 EEL EEL EEL CC 1 EEL CC 1 Soil Boring Soil Boring ELBS1012 ELBS1012 ELBS1012S010 ELBS1012S010 Primary Sample Primary Sample 3/26/08 10:30 Soil 3/26/08 10:30 Soil EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Result  Value  Units Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 9045C 9056 tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH Bromide 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 24959679 4.8 1.9 1.9 1.9 1.9 1.9 4.8 1.9 1.7 98 98 260 98 8.9 0.4 1 In Place Primary Result Inorganics 9056 Chloride 16887006 5.2 mg/kg 0.5 0.5 1 In Place 1 In Place Primary Result Primary Result Inorganics Inorganics 9056 9056 Fluoride Nitrate‐N 16984488 NO3N Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 Page 9 of 108 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg Result  in SL Units 0.0048 0.0019 0.0019 0.0019 0.0019 0.0019 0.0048 0.0019 0.0017 98 98 260 98 8.9 5.2 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg Detected Project  Qual  Code Validation Note N N N N N N N N N N N Y N Y N UJ UJ UJ UJ UJ UJ UJ UJ U U U $,H $,H $,H $,H $,H $,H $,H $,H U $ 5.2 mg/kg N U 5.2 mg/kg 0.95 mg/kg 5.2 mg/kg 0.95 mg/kg N Y U J 5.2 0.57 13 7200 100 0.53 1 7.5 4.4 8.5 3000 240 29 33 0.78 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.2 0.57 13 7200 100 0.53 5.2 7.5 4.4 8.5 3000 240 29 33 0.78 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y N Y Y Y Y Y Y Y Y U J B, result changed from 4.8 and  MDL from 2 F, result changed from 0.9 and  MDL from 0.85 H F, result changed from 0.48  and MDL from 0.35 H J A 1 0.73 0.035 7.7 1.8 0.41 4.5 0.12 0.67 0.097 0.0057 4.2 4.2 400 13 400 400 400 99 400 400 400 400 400 400 400 7.8 16 16 35 8.6 400 400 400 400 400 6.1 0.84 1.7 1.7 4.2 1.7 1.7 4.2 1.7 4.2 0.84 1.7 4.2 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 4.2 42 8.4 4.2 8.4 1.7 4.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1 0.73 0.035 7.7 1.8 0.41 4.5 0.12 0.67 0.097 0.031 0.0042 0.0042 0.4 0.013 0.4 0.4 0.4 0.099 0.4 0.4 0.4 0.4 0.4 0.4 0.4 0.0078 0.016 0.016 0.035 0.0086 0.4 0.4 0.4 0.4 0.4 0.0061 0.00084 0.0017 0.0017 0.0042 0.0017 0.0017 0.0042 0.0017 0.0042 0.00084 0.0017 0.0042 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0042 0.042 0.0084 0.0042 0.0084 0.0017 0.0042 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y N N N N Y N N N Y N N N N N N N Y Y Y Y Y N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N $ $ U U J A J A J A J U J J J J J J U UJ UJ U J U U U J U U U U U U U J J J J J U U U U U J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ B, result changed from 0.085  and MDL from 0.013 A,Q Q Q Q $,H $,H $ $ $ $ $ $ $ $ $ $ $ *III $ $ $ $ $ $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Boeing Soil Char Level  (mg/kg) 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No No No No SL No No No No No No No Yes No SL No SL Ratio Boeing Soil Char Level 4.36E‐03 4.57E‐03 3.22E‐05 2.23E‐05 No SL 2.38E‐03 2.82E‐05 9.31E‐02 5.00E‐04 7.00E‐02 7.00E‐02 1.86E‐01 9.80E+01 No SL No SL ‐‐ No SL No SL 35 2340 No No ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 SCL Basis Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL SCL Units RL RL Units mg/kg 5.2 mg/kg 5.2 mg/kg Y Y Y 1.49E‐01 Ecological RBSL 4.06E‐04 Ecological RBSL mg/kg mg/kg 5.2 mg/kg 5.2 mg/kg 5.2 mg/kg 0.33 mg/kg Y Y Y Y Y Y No SL No No SL No No No No No No No No No No No No No SL 6.60E‐04 No SL 1.90E‐01 4.91E‐01 1.10E‐01 2.36E‐01 1.25E‐01 1.68E‐01 1.32E‐01 3.99E‐01 3.18E‐01 2.59E‐01 2.16E‐01 7.33E‐02 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.2 5.2 5.2 10 0.52 0.31 5.2 1 0.52 6.5 100 120 1 5.2 26 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.2 0.52 1.8 5.1 0.25 0.16 1 0.41 0.1 0.31 42 61 0.64 1 0.7 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Yes No No No No No No No No No No No No Yes No No No Yes No Yes No No No Yes No Yes No No No No No No No Yes No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No 2.00E+00 3.02E‐02 8.05E‐02 1.83E‐01 5.31E‐02 2.50E‐01 7.01E‐02 1.20E‐01 6.77E‐01 1.27E‐01 3.56E‐02 4.20E‐04 1.91E‐01 1.25E+00 1.44E‐04 1.74E‐01 8.89E‐02 3.64E+00 7.62E‐03 1.23E+01 5.49E‐02 7.55E‐03 3.64E‐01 1.21E+00 1.82E‐01 1.03E+00 2.02E‐01 4.13E‐02 2.16E‐03 2.92E‐02 7.61E‐02 7.41E‐03 4.49E‐01 1.03E+00 2.74E‐02 3.08E‐01 5.08E‐03 2.93E‐04 6.91E‐07 5.90E‐03 1.91E‐05 3.19E‐03 8.99E‐04 6.09E‐04 No SL 4.20E‐04 No SL 5.48E‐04 4.29E‐02 1.63E‐02 1.31E‐05 6.51E‐03 3.87E‐03 5.31E‐04 7.39E‐05 No SL 1.28E‐03 No SL 4.20E+00 3.65E‐04 9.33E‐04 1.83E‐04 1.48E‐02 1.68E‐04 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1 0.52 0.21 0.21 0.41 0.1 0.41 1 0.21 0.21 0.031 4.2 4.2 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 400 0.84 1.7 1.7 4.2 1.7 1.7 4.2 1.7 4.2 0.84 1.7 4.2 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 4.2 42 8.4 4.2 8.4 1.7 4.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1 0.015 0.0063 0.084 0.052 0.017 0.041 0.083 0.0046 0.0031 0.0057 0.37 0.49 66 3.3 5.9 9.3 17 6.4 9.2 5.2 6.2 3.2 3.4 2.7 2.9 2.9 2.9 4 3.8 4.8 4.2 4.5 4.9 6.5 6.2 3.5 0.6 0.46 0.58 0.38 0.76 0.49 0.58 0.5 0.47 0.65 0.54 0.49 0.5 0.47 0.59 0.5 0.53 0.54 0.5 0.6 0.52 4.2 1.5 0.88 3.2 0.45 0.51 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA 4.8 1.9 1.9 1.9 1.9 1.9 4.8 1.9 1.7 98 98 98 98 0.1 5.2 Background 0.55 0.77 0.69 0.42 0.45 0.58 0.46 0.3 1.1 20 20 20 20 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg MDL 0.4 mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1012 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1012S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1013 ELBS1013 ELBS1013 ELBS1013S010 ELBS1013S010 ELBS1013S010 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 Collection  Date 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 3/26/08 10:30 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 Matrix  Type Sample Top  Depth (feet bgs) Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 0 0 0 Primary Sample Primary Sample Primary Sample 4/11/08 8:46 Soil 4/11/08 8:46 Soil 4/11/08 8:46 Soil 0 0 0 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Result  Value  Units Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 300.0 300.0 Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide Chloride 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 16887006 4.2 1.7 4.2 4.2 0.84 1.7 4.2 1.7 4.2 4.2 1.7 1.7 1.7 1.7 0.84 4.2 1.7 8.4 4.2 4.2 1.7 4.2 1.7 4.2 1.7 4.2 1.7 4.2 0.84 1.7 4.2 1.7 1.7 1.7 1.7 1.7 4.2 1.7 1.83 3.79 3.79 12.9 3.79 0.687 0.687 1 In Place 1 In Place 1 In Place Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics 300.0 300.0 300.0 Fluoride Nitrate‐N Nitrite‐NO2 16984488 NO3N NO2 1.04 mg/kg 0.312 mg/kg 0.312 mg/kg 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH 300.0 300.0 9045C 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Ortho Phosphate (as PO4) Sulfate pH Aluminum Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene 14265442 14808798 E‐10139 7429905 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Page 10 of 108 2.08 8.05 8.41 12200 0.342 1.1 2650 164 4 132 0.77 0.34 22.2 7.5 11.8 7.6 20.4 0.56 14 0.55 0.061 0.3 50.8 54.6 3.5 0.0025 0.917 0.917 28.7 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0042 0.0017 0.0042 0.0042 0.00084 0.0017 0.0042 0.0017 0.0042 0.0042 0.0017 0.0017 0.0017 0.0017 0.00084 0.0042 0.0017 0.0084 0.0042 0.0042 0.0017 0.0042 0.0017 0.0042 0.0017 0.0042 0.0017 0.0042 0.00084 0.0017 0.0042 0.0017 0.0017 0.0017 0.0017 0.0017 0.0042 0.0017 0.00183 3.79 3.79 12.9 3.79 2.08 2.08 SL Units Detected Project  Qual  Code Validation Note mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U U U 1.04 mg/kg 1.04 mg/kg 1.04 mg/kg N N N U U U N Y Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N N Y N N N N N N N N N N N N N N N N N N N N N N U $ $ F, result changed from 0.905  and MDL from 0.312 $ $ B, result changed from 1.13  and MDL from 0.687 UJ UJ I I J J J Q,A Q,A Q,A J Q J U J Q,A J U U B, B, B, B 2.08 8.05 8.41 12200 1.1 5.52 2650 164 4 132 0.77 0.34 22.2 7.5 11.8 7.6 20.4 0.56 14 1.1 0.061 0.3 50.8 54.6 3.5 0.0025 0.000917 0.000917 0.0287 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 0.0189 mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg U U U U U U U U U U U U U U U U U U U U U U U U U $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Boeing Soil Char Level  (mg/kg) ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No No No Yes No SL No SL 35 2340 ‐‐ No No No SL 863.2 ‐‐ ‐‐ 37900 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 0.761 111.8 153 10.64 0.87 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 No No SL No SL No Yes No No No No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level No SL 8.72E‐03 1.83E‐04 1.31E‐03 1.18E‐02 8.10E‐05 No SL 2.32E‐03 1.31E‐03 No SL 1.84E‐04 No SL 1.31E‐03 2.34E‐04 3.77E‐05 1.02E‐04 7.36E‐04 1.03E‐06 No SL 1.41E‐03 5.15E‐04 6.89E‐05 2.33E‐05 2.63E‐04 5.00E‐04 2.63E‐04 4.59E‐04 4.29E‐03 No SL 8.10E‐06 3.82E‐03 4.09E‐03 2.88E‐05 1.99E‐05 No SL 2.13E‐03 2.47E‐05 8.33E‐02 5.38E‐04 2.71E‐03 2.71E‐03 9.21E‐03 3.79E+00 No SL No SL SCL Basis SCL Units RL RL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.2 1.7 4.2 4.2 0.84 1.7 4.2 1.7 4.2 4.2 1.7 1.7 1.7 1.7 0.84 4.2 1.7 8.4 4.2 4.2 1.7 4.2 1.7 4.2 1.7 4.2 1.7 4.2 0.84 1.7 4.2 1.7 1.7 1.7 1.7 1.7 4.2 1.7 1.83 3.79 3.79 3.79 3.79 2.08 2.08 2.97E‐02 Ecological RBSL 4.44E‐04 Ecological RBSL No SL mg/kg mg/kg mg/kg 1.04 mg/kg 1.04 mg/kg 1.04 mg/kg 2.41E‐03 No SL No SL 3.22E‐01 2.20E+00 2.51E‐01 3.52E‐01 2.18E‐01 1.65E‐01 6.48E‐01 1.60E‐01 7.82E‐01 3.69E‐01 2.86E‐01 2.81E‐01 2.24E‐01 3.17E‐01 3.41E‐01 2.18E‐01 1.10E+00 6.16E‐02 3.94E‐01 4.54E‐01 3.57E‐01 3.29E‐01 2.87E‐03 9.17E‐05 4.17E‐02 8.97E‐02 2.10E‐04 8.22E‐03 4.20E‐03 1.72E‐01 1.45E‐03 5.82E‐01 2.59E‐03 3.57E‐04 1.72E‐02 5.73E‐02 8.59E‐03 4.88E‐02 4.88E‐01 4.88E‐02 2.55E‐03 4.88E‐02 1.58E‐02 1.67E‐01 3.50E‐04 2.12E‐02 4.88E‐02 1.29E‐03 mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL 2.08 4.16 0.1 22.1 1.1 5.52 16.6 16.6 1.1 0.44 0.11 0.22 0.659 0.22 0.22 0.44 2.2 0.11 0.44 1.1 0.22 0.22 11 2.2 0.44 0.0111 0.917 0.917 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 0.52 0.45 0.45 0.46 0.42 0.56 0.59 0.54 0.37 0.73 0.55 0.23 0.55 0.59 0.39 0.31 0.68 1.6 1.1 0.74 1.1 0.5 0.43 0.51 0.63 0.66 0.45 0.44 0.38 0.56 0.48 0.67 0.6 0.37 0.39 0.5 0.4 0.26 0.229 1.25 1.25 1.25 1.25 0.687 0.687 MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 1.04 mg/kg 0.312 mg/kg 0.312 mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 2.08 1.04 0.01 7.5 0.342 1.1 5.52 4.97 0.33 0.11 0.022 0.022 0.22 0.022 0.044 0.11 0.44 0.022 0.11 0.55 0.044 0.044 2.2 0.44 0.11 0.00166 0.275 0.458 6.24 5.67 5.67 5.67 5.67 5.67 3.78 5.67 3.78 6.32 5.67 3.78 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S010 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 8:46 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 5 5 5 EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1013 ELBS1013 ELBS1013 ELBS1013S060 ELBS1013S060 ELBS1013S060 Primary Sample Primary Sample Primary Sample 4/11/08 9:03 Soil 4/11/08 9:03 Soil 4/11/08 9:03 Soil 5 5 5 EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1013 ELBS1013 ELBS1013 ELBS1013S060 ELBS1013S060 ELBS1013S060 Primary Sample Primary Sample Primary Sample 4/11/08 9:03 Soil 4/11/08 9:03 Soil 4/11/08 9:03 Soil EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Inorganics Inorganics Inorganics 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 300.0 300.0 300.0 300.0 300.0 Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide Chloride Fluoride Nitrate‐N Nitrite‐NO2 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 16887006 16984488 NO3N NO2 18.9 18.9 0.917 0.917 0.917 4.58 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 4.58 4.58 0.917 4.58 0.917 4.58 4.58 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 1.83 2.7 0.917 0.917 0.917 0.917 0.917 0.917 0.235 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 1.83 3.77 3.77 3.77 3.77 0.709 2.45 2.17 2.45 0.322 6 In Place 6 In Place 6 In Place Primary Result Primary Result Primary Result Inorganics Inorganics Metals 300.0 300.0 6010B Ortho Phosphate (as PO4) Sulfate Aluminum 14265442 14808798 7429905 5 5 5 6 In Place 6 In Place 6 In Place Primary Result Primary Result Primary Result Metals Metals Metals 6010B 6010B 6010B Antimony Boron Potassium 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Page 11 of 108 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units Detected Project  Qual  Code Validation Note mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N Y N N N N N N N N N N N N N N Y Y Y N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U J U U U U U U U U U U U U U U 2.15 mg/kg 26.3 mg/kg 12300 mg/kg 2.15 mg/kg 26.3 mg/kg 12300 mg/kg N Y Y U $ B, result changed from 1.11  and MDL from 0.709 7440360 7440428 7440097 0.351 mg/kg 1.11 mg/kg 1630 mg/kg 1.11 mg/kg 5.54 mg/kg 1630 mg/kg N N Y UJ UJ I,$, MDL and result changed  from 0.344 I 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 7440280 7440622 7440666 153 5 118 0.61 0.21 21.1 5.5 9.6 5.6 25.9 0.21 14 0.56 0.091 0.24 49.8 52.7 153 5 118 0.61 0.21 21.1 5.5 9.6 5.6 25.9 0.21 14 1.12 0.091 0.24 49.8 52.7 N Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y U F, RL changed from 16.6 and  MDL from 4.99 J J J J Q,A Q,A Q,A J Q J U J Q,A mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.0189 0.0189 0.000917 0.000917 0.000917 0.00458 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.00458 0.00458 0.000917 0.00458 0.000917 0.00458 0.00458 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.00183 0.0027 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000235 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.000917 0.00183 3.77 3.77 3.77 3.77 2.15 2.45 2.17 2.45 1.07 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg U $ Boeing Soil Char Level  (mg/kg) 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ 35 2340 ‐‐ Exceeds Boeing Soil Char Level No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No No No Yes No SL No SL No No No SL 863.2 ‐‐ 37900 No No SL No 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 0.761 111.8 153 Ratio Boeing Soil Char Level 1.45E‐02 1.58E‐02 3.20E‐04 3.73E‐07 3.18E‐03 2.08E‐05 1.72E‐03 4.85E‐04 1.33E‐04 No SL 9.17E‐05 No SL 2.96E‐04 9.38E‐03 8.82E‐03 7.05E‐06 3.51E‐03 2.09E‐03 2.87E‐04 3.99E‐05 No SL 6.89E‐04 No SL 5.61E‐07 4.58E‐01 5.73E‐05 1.99E‐04 5.73E‐05 1.02E‐03 9.96E‐05 7.97E‐03 3.67E‐05 No SL 4.70E‐03 3.99E‐05 2.87E‐04 1.29E‐02 4.37E‐05 No SL 1.25E‐03 2.87E‐04 9.95E‐05 No SL 1.26E‐04 4.11E‐05 2.24E‐05 3.97E‐04 7.05E‐04 5.55E‐04 9.09E‐04 No SL 1.50E‐05 1.26E‐05 2.70E‐04 2.48E‐04 9.36E‐04 1.12E‐06 8.34E‐04 2.20E‐03 1.55E‐05 1.08E‐05 No SL 1.15E‐03 5.39E‐06 4.50E‐02 5.38E‐04 2.69E‐03 2.69E‐03 2.69E‐03 3.77E+00 No SL No SL 6.20E‐02 1.05E‐03 No SL SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 18.9 18.9 0.917 0.917 0.917 4.58 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 4.58 4.58 0.917 4.58 0.917 4.58 4.58 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 1.83 4.58 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 0.917 1.83 3.77 3.77 3.77 3.77 2.15 2.15 1.07 1.07 1.07 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL 5.67 5.94 0.183 0.275 0.229 0.917 0.275 0.275 0.275 0.229 0.229 0.458 0.183 0.458 0.183 0.183 0.229 0.275 0.183 0.183 0.275 0.183 0.275 1.56 1.15 0.183 1.39 0.22 0.999 2.36 0.302 0.183 0.458 0.183 0.275 0.458 0.183 0.183 0.458 0.183 0.458 0.275 0.183 0.275 0.275 0.458 0.183 0.183 0.229 1.83 0.183 0.183 0.183 0.183 0.229 0.183 0.183 0.183 0.183 0.266 0.275 0.275 0.229 0.458 0.458 0.228 1.24 1.24 1.24 1.24 0.709 0.709 0.322 0.322 0.322 MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 2.49E‐03 Background No SL 3.25E‐01 Background mg/kg mg/kg mg/kg 2.15 mg/kg 4.3 mg/kg 22.2 mg/kg 2.15 mg/kg 1.07 mg/kg 7.54 mg/kg Y Y Y Y Y Y Y Y Y Yes No No 2.22E+00 MRL 2.52E‐01 Ecological RBSL 2.17E‐01 Background mg/kg mg/kg mg/kg 1.11 mg/kg 5.54 mg/kg 16.6 mg/kg 0.351 mg/kg 1.11 mg/kg 5.54 mg/kg Y Y Y Y Y Y Y Y Y No No No No No No No No No No No No Yes No No No No 2.03E‐01 2.07E‐01 5.79E‐01 1.27E‐01 4.83E‐01 3.51E‐01 2.10E‐01 2.29E‐01 1.65E‐01 4.02E‐01 1.28E‐01 2.18E‐01 1.12E+00 9.19E‐02 3.15E‐01 4.45E‐01 3.44E‐01 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background 153 1.12 0.448 0.112 0.224 0.672 0.224 0.224 0.448 2.24 0.112 0.448 1.12 0.224 0.224 11.2 2.24 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 153 0.336 0.112 0.0224 0.0224 0.224 0.0224 0.0448 0.112 0.448 0.0224 0.112 0.56 0.0448 0.0448 2.24 0.448 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1013 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1013S060 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 4/11/08 9:03 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Analysis  Method 6020 7471A 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9045C 9056 9056 9056 9056 9056 9056 9056 Analyte Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Bromide Chloride Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Page 12 of 108 CAS Number 7440677 7439976 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 24959679 16887006 16984488 NO3N NO2 14265442 14808798 Result  Value 2.8 0.0091 0.914 0.914 50.3 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 0.914 0.914 0.914 4.57 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 4.57 4.57 0.914 4.57 0.914 4.57 4.57 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 1.83 2.81 0.914 0.914 0.914 0.914 0.914 0.914 0.255 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 1.9 7.7 0.44 7.8 2.2 1.1 0.82 0.6 12 Result  Value  Units mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 2.8 mg/kg 0.0091 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.0503 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.0189 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.00457 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.00457 mg/kg 0.00457 mg/kg 0.000914 mg/kg 0.00457 mg/kg 0.000914 mg/kg 0.00457 mg/kg 0.00457 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.00183 mg/kg 0.00281 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000255 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.000914 mg/kg 0.0019 mg/kg 7.7 ph Units 5.7 mg/kg 5.7 mg/kg 2.2 mg/kg 1.1 mg/kg 0.82 mg/kg 0.6 mg/kg 12 mg/kg Detected Y Y N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N Y N N N N N N N N N Y N N Y Y Y Y Y Project  Qual  Code J U U Validation Note B, B, B, B U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U J U U U U U U U U U U U J J J J B H H H Boeing Soil Char Level  (mg/kg) 10.64 0.87 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No SL No SL No SL No No No SL No No SL Ratio Boeing Soil Char Level 2.63E‐01 1.05E‐02 9.14E‐05 4.15E‐02 1.57E‐01 2.10E‐04 8.22E‐03 4.20E‐03 1.72E‐01 1.45E‐03 5.82E‐01 2.59E‐03 3.57E‐04 1.72E‐02 5.73E‐02 8.59E‐03 4.88E‐02 4.88E‐01 4.88E‐02 2.55E‐03 4.88E‐02 1.58E‐02 1.67E‐01 3.50E‐04 2.12E‐02 4.88E‐02 1.29E‐03 1.45E‐02 1.58E‐02 3.18E‐04 3.72E‐07 3.17E‐03 2.08E‐05 1.71E‐03 4.84E‐04 1.32E‐04 No SL 9.14E‐05 No SL 2.95E‐04 9.35E‐03 8.79E‐03 7.03E‐06 3.50E‐03 2.08E‐03 2.86E‐04 3.97E‐05 No SL 6.87E‐04 No SL 5.60E‐07 4.57E‐01 5.71E‐05 1.99E‐04 5.71E‐05 1.02E‐03 9.93E‐05 7.95E‐03 3.66E‐05 No SL 4.69E‐03 3.97E‐05 2.86E‐04 1.29E‐02 4.35E‐05 No SL 1.25E‐03 2.86E‐04 9.91E‐05 No SL 1.26E‐04 4.10E‐05 2.23E‐05 3.96E‐04 7.03E‐04 5.55E‐04 9.46E‐04 No SL 1.50E‐05 1.25E‐05 2.69E‐04 2.47E‐04 9.33E‐04 1.21E‐06 8.31E‐04 2.20E‐03 1.55E‐05 1.07E‐05 No SL 1.15E‐03 5.38E‐06 4.48E‐02 5.59E‐04 No SL No SL No SL 6.29E‐02 4.70E‐04 No SL 6.95E‐04 No SL SCL Basis Background Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 0.448 0.011 0.914 0.914 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 18.9 0.914 0.914 0.914 4.57 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 4.57 4.57 0.914 4.57 0.914 4.57 4.57 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 1.83 4.57 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 1.9 0.1 5.7 5.7 5.7 5.7 5.7 5.7 5.7 MDL  Units RL Units MDL mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.112 0.00165 0.274 0.457 6.25 5.68 5.68 5.68 5.68 5.68 3.79 5.68 3.79 6.33 5.68 3.79 5.68 5.68 5.68 5.68 5.68 5.68 5.68 5.68 5.68 5.68 5.68 5.68 5.95 0.183 0.274 0.228 0.914 0.274 0.274 0.274 0.228 0.228 0.457 0.183 0.457 0.183 0.183 0.228 0.274 0.183 0.183 0.274 0.183 0.274 1.55 1.14 0.183 1.39 0.219 0.996 2.36 0.302 0.183 0.457 0.183 0.274 0.457 0.183 0.183 0.457 0.183 0.457 0.274 0.183 0.274 0.274 0.457 0.183 0.183 0.228 1.83 0.183 0.183 0.183 0.183 0.228 0.183 0.183 0.183 0.183 0.265 0.274 0.274 0.228 0.457 0.457 1.2 mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.44 2.3 0.94 0.36 0.38 0.57 2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N Y Y Y Y N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014D010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Analysis  Method 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9045C 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B Analyte Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Bromide Chloride Fluoride Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Page 13 of 108 CAS Number 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 24959679 16887006 16984488 NO2 14265442 14808798 7429905 7440393 7440417 Result  Value 12000 120 0.94 1.1 16 5.6 12 2700 130 32 40 1 0.2 2.3 0.26 11 5.6 0.49 12 0.39 0.036 0.28 0.0063 4.7 4.7 0.95 1.9 1.9 4.7 1.9 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.7 47 9.5 4.7 9.5 1.9 4.7 4.7 1.9 4.7 4.7 0.95 1.9 4.7 1.9 4.7 4.7 1.9 1.9 1.9 1.9 0.95 4.7 1.9 9.5 4.7 4.7 1.9 4.7 1.9 4.7 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 4.7 1.9 1.8 7.4 0.43 8.2 2.1 0.6 0.74 24 12000 100 0.92 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 12000 120 0.94 1.1 16 5.6 12 2700 130 32 40 29 0.2 2.3 0.26 11 5.6 0.49 12 0.39 0.036 0.28 0.034 0.0047 0.0047 0.00095 0.0019 0.0019 0.0047 0.0019 0.0019 0.0047 0.0019 0.0047 0.00095 0.0019 0.0047 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0047 0.047 0.0095 0.0047 0.0095 0.0019 0.0047 0.0047 0.0019 0.0047 0.0047 0.00095 0.0019 0.0047 0.0019 0.0047 0.0047 0.0019 0.0019 0.0019 0.0019 0.00095 0.0047 0.0019 0.0095 0.0047 0.0047 0.0019 0.0047 0.0019 0.0047 0.0019 0.0047 0.0019 0.0047 0.00095 0.0019 0.0047 0.0019 0.0019 0.0019 0.0019 0.0019 0.0047 0.0019 0.0018 7.4 5.5 5.5 2.1 0.6 0.74 24 12000 100 0.92 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N Y Y Y Y Y Y Y Project  Qual  Code Validation Note Q, Q J B J U J J J U U U U U U U U U UJ U U U U U U U U U U UJ U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U U U J J J F B Q, Q B B L B Q Q, Q Q, Q, B F F Q, Q Q, Q B H H Q, Q Boeing Soil Char Level  (mg/kg) 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ ‐‐ ‐‐ 35 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 Exceeds Boeing Soil Char Level No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No SL No SL No No SL No No SL No No No Ratio Boeing Soil Char Level 3.17E‐01 5.89E‐01 1.96E‐01 5.00E‐02 2.66E‐01 2.14E‐01 1.86E‐01 3.59E‐01 1.72E‐01 2.86E‐01 2.61E‐01 2.73E+00 4.00E‐01 9.50E‐02 5.98E‐01 2.62E‐01 1.65E‐01 2.98E‐01 1.87E‐01 3.90E‐01 3.64E‐02 3.68E‐01 3.91E‐02 4.70E‐04 2.14E‐01 3.31E‐04 7.72E‐07 6.60E‐03 2.14E‐05 3.56E‐03 1.01E‐03 6.81E‐04 No SL 4.70E‐04 No SL 6.13E‐04 4.81E‐02 1.83E‐02 1.46E‐05 7.28E‐03 4.33E‐03 5.94E‐04 8.26E‐05 No SL 1.43E‐03 No SL 4.70E+00 4.13E‐04 1.04E‐03 2.07E‐04 1.65E‐02 1.88E‐04 No SL 9.74E‐03 2.04E‐04 1.47E‐03 1.34E‐02 9.05E‐05 No SL 2.59E‐03 1.47E‐03 No SL 2.06E‐04 No SL 1.46E‐03 2.61E‐04 4.26E‐05 1.15E‐04 8.23E‐04 1.16E‐06 No SL 1.58E‐03 5.76E‐04 7.70E‐05 2.60E‐05 2.94E‐04 5.59E‐04 2.94E‐04 5.14E‐04 4.80E‐03 No SL 9.05E‐06 4.27E‐03 4.57E‐03 3.22E‐05 2.23E‐05 No SL 2.38E‐03 2.76E‐05 9.31E‐02 5.29E‐04 No SL No SL No SL 6.00E‐02 No SL 8.57E‐04 No SL 3.17E‐01 4.91E‐01 1.92E‐01 SCL Basis Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 11 0.57 0.34 5.7 1.1 0.57 7.2 110 140 1.1 5.7 29 1.1 0.57 0.23 0.23 0.46 0.11 0.46 1.1 0.23 0.23 0.034 4.7 4.7 0.95 1.9 1.9 4.7 1.9 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.7 47 9.5 4.7 9.5 1.9 4.7 4.7 1.9 4.7 4.7 0.95 1.9 4.7 1.9 4.7 4.7 1.9 1.9 1.9 1.9 0.95 4.7 1.9 9.5 4.7 4.7 1.9 4.7 1.9 4.7 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 4.7 1.9 1.8 0.1 5.5 5.5 5.5 5.5 5.5 5.5 11 0.55 0.33 MDL  Units RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.6 0.27 0.17 1.1 0.46 0.11 0.34 47 67 0.71 1.1 0.78 0.014 0.017 0.007 0.093 0.057 0.018 0.046 0.091 0.0051 0.0034 0.0063 0.42 0.55 0.67 0.52 0.65 0.43 0.85 0.55 0.65 0.57 0.53 0.73 0.61 0.55 0.56 0.53 0.66 0.57 0.6 0.61 0.56 0.67 0.59 4.7 1.7 1 3.6 0.51 0.58 0.59 0.51 0.51 0.52 0.47 0.64 0.66 0.61 0.42 0.83 0.63 0.27 0.62 0.66 0.44 0.35 0.77 1.8 1.2 0.83 1.2 0.57 0.48 0.58 0.71 0.75 0.51 0.49 0.43 0.64 0.54 0.76 0.68 0.42 0.45 0.57 0.46 0.29 1.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.43 2.2 0.91 0.37 0.56 1.9 5.4 0.27 0.17 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N N N Y N N N N N Y N N N N Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N N N Y Y Y N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S010 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:20 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Analyte Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Bromide Chloride Fluoride Nitrite‐NO2 Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Page 14 of 108 CAS Number 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 24959679 16887006 16984488 NO2 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 Result  Value 1.6 16 5.7 14 3000 120 32 45 1.9 0.29 3.5 0.23 11 9.2 0.56 12 0.37 0.057 0.27 0.0061 4.5 4.5 0.91 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.91 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 9.1 4.5 9.1 1.8 4.5 4.5 1.8 4.5 4.5 0.91 1.8 4.5 1.8 4.5 4.5 1.8 1.8 1.8 1.8 0.91 4.5 1.8 9.1 4.5 4.5 1.8 4.5 1.8 4.5 1.8 4.5 1.8 4.5 0.91 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 1.8 0.43 5.8 1.9 0.58 12 15000 110 1.3 1.1 31 10 39 2400 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 1.6 16 5.7 14 3000 550 32 45 1.9 0.29 3.5 0.23 11 9.2 0.56 12 0.37 0.057 0.27 0.033 0.0045 0.0045 0.00091 0.0018 0.0018 0.0045 0.0018 0.0018 0.0045 0.0018 0.0045 0.00091 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.045 0.0091 0.0045 0.0091 0.0018 0.0045 0.0045 0.0018 0.0045 0.0045 0.00091 0.0018 0.0045 0.0018 0.0045 0.0045 0.0018 0.0018 0.0018 0.0018 0.00091 0.0045 0.0018 0.0091 0.0045 0.0045 0.0018 0.0045 0.0018 0.0045 0.0018 0.0045 0.0018 0.0045 0.00091 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.0018 0.0018 5.5 5.5 1.9 0.58 12 15000 110 1.3 5.5 31 10 39 2400 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y N Y Y Y Y Project  Qual  Code Validation Note J B U J J J J U U U U U U U U U UJ U U U U U U U U U U UJ U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U U U J J F B Q, Q B B L B Q Q, Q Q, Q, B F F Q, Q Q, Q B H Q, Q U B Boeing Soil Char Level  (mg/kg) 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ ‐‐ 35 ‐‐ ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No SL No No SL No SL No No No No No No No No Ratio Boeing Soil Char Level 7.27E‐02 2.66E‐01 2.18E‐01 2.17E‐01 3.99E‐01 7.29E‐01 2.86E‐01 2.94E‐01 1.79E‐01 5.80E‐01 1.45E‐01 5.29E‐01 2.62E‐01 2.71E‐01 3.41E‐01 1.87E‐01 3.70E‐01 5.76E‐02 3.55E‐01 3.79E‐02 4.50E‐04 2.05E‐01 3.17E‐04 7.32E‐07 6.25E‐03 2.05E‐05 3.38E‐03 9.52E‐04 6.52E‐04 No SL 4.50E‐04 No SL 5.81E‐04 4.60E‐02 1.73E‐02 1.38E‐05 6.90E‐03 4.10E‐03 5.63E‐04 7.83E‐05 No SL 1.35E‐03 No SL 4.50E+00 3.96E‐04 1.00E‐03 1.98E‐04 1.57E‐02 1.80E‐04 No SL 9.23E‐03 1.96E‐04 1.41E‐03 1.28E‐02 8.57E‐05 No SL 2.46E‐03 1.41E‐03 No SL 1.95E‐04 No SL 1.38E‐03 2.47E‐04 4.08E‐05 1.10E‐04 7.79E‐04 1.12E‐06 No SL 1.52E‐03 5.45E‐04 7.38E‐05 2.47E‐05 2.81E‐04 5.29E‐04 2.81E‐04 4.86E‐04 4.59E‐03 No SL 8.57E‐06 4.09E‐03 4.33E‐03 3.05E‐05 2.11E‐05 No SL 2.26E‐03 2.65E‐05 8.82E‐02 5.29E‐04 No SL No SL 5.43E‐02 No SL No SL 3.96E‐01 5.40E‐01 2.71E‐01 2.50E‐01 5.16E‐01 3.82E‐01 6.06E‐01 3.19E‐01 SCL Basis Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.5 1.1 0.55 7 110 550 1.1 5.5 28 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 4.5 4.5 0.91 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.91 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 9.1 4.5 9.1 1.8 4.5 4.5 1.8 4.5 4.5 0.91 1.8 4.5 1.8 4.5 4.5 1.8 1.8 1.8 1.8 0.91 4.5 1.8 9.1 4.5 4.5 1.8 4.5 1.8 4.5 1.8 4.5 1.8 4.5 0.91 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 1.8 5.5 5.5 5.5 5.5 5.5 11 0.55 0.33 5.5 1.1 0.55 6.9 110 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.1 0.44 0.11 0.33 45 65 0.69 1.1 0.75 0.014 0.016 0.0068 0.09 0.055 0.018 0.044 0.089 0.0049 0.0033 0.0061 0.4 0.53 0.64 0.5 0.63 0.41 0.82 0.53 0.63 0.54 0.51 0.7 0.58 0.53 0.54 0.51 0.64 0.54 0.57 0.58 0.54 0.64 0.56 4.5 1.6 0.95 3.5 0.49 0.55 0.56 0.49 0.49 0.5 0.45 0.61 0.64 0.58 0.4 0.79 0.6 0.25 0.59 0.64 0.42 0.34 0.74 1.8 1.1 0.8 1.2 0.54 0.46 0.55 0.68 0.72 0.49 0.47 0.41 0.61 0.52 0.73 0.65 0.4 0.43 0.54 0.44 0.28 1.2 0.43 2.2 0.9 0.37 1.9 5.4 0.26 0.16 1.1 0.44 0.11 0.33 45 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y N Y Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Sample  Bottom  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1014 ELBS1015 ELBS1015 ELBS1015 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1014S050 ELBS1015S010 ELBS1015S010 ELBS1015S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 3/24/08 10:30 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 1 1 1 EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015S010 ELBS1015S010 ELBS1015S010 Primary Sample Primary Sample Primary Sample 4/8/08 9:00 Soil 4/8/08 9:00 Soil 4/8/08 9:00 Soil 0.5 0.5 0.5 1 In Place 1 In Place 1 In Place Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics 300.0 300.0 300.0 Fluoride Nitrate‐N Nitrite‐NO2 16984488 NO3N NO2 EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 Primary Sample Primary Sample Primary Sample Primary Sample 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 Soil Soil Soil Soil 0.5 0.5 0.5 0.5 1 1 1 1 In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Metals 300.0 300.0 9045C 6010B Ortho Phosphate (as PO4) Sulfate pH Aluminum EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals 6010B 6010B 6010B 6010B 6020 Antimony Boron Potassium Sodium Arsenic RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Inorganics 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 300.0 300.0 Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Bromide Chloride 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 24959679 16887006 Page 15 of 108 Result  Value Result  Value  Units Result  in SL Units SL Units Detected Project  Qual  Code 120 47 62 0.75 0.22 52 0.11 13 8.4 0.29 22 0.25 0.03 0.29 0.0061 4.6 4.6 0.92 1.8 1.8 4.6 1.8 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.6 46 9.2 4.6 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 130 47 62 27 0.22 52 0.11 13 8.4 0.29 22 0.25 0.03 0.29 0.033 0.0046 0.0046 0.00092 0.0018 0.0018 0.0046 0.0018 0.0018 0.0046 0.0018 0.0046 0.00092 0.0018 0.0046 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0046 0.046 0.0092 0.0046 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y N Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N 9.2 1.8 4.6 4.6 1.8 4.6 4.6 0.92 1.8 4.6 1.8 4.6 4.6 1.8 1.8 1.8 1.8 0.92 4.6 1.8 9.2 4.6 4.6 1.8 4.6 1.8 4.6 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 1.8 4.6 1.8 2.21 1.06 3.75 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 0.0092 0.0018 0.0046 0.0046 0.0018 0.0046 0.0046 0.00092 0.0018 0.0046 0.0018 0.0046 0.0046 0.0018 0.0018 0.0018 0.0018 0.00092 0.0046 0.0018 0.0092 0.0046 0.0046 0.0018 0.0046 0.0018 0.0046 0.0018 0.0046 0.0018 0.0046 0.00092 0.0018 0.0046 0.0018 0.0018 0.0018 0.0018 0.0018 0.0046 0.0018 0.00221 1.06 3.75 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U J 2.78 mg/kg 1.54 mg/kg 0.338 mg/kg 2.78 mg/kg 1.54 mg/kg 1.13 mg/kg N Y N U 14265442 14808798 E‐10139 7429905 3.46 4.06 8.34 9370 mg/kg mg/kg pH Units mg/kg 3.46 4.06 8.34 9370 mg/kg mg/kg ph Units mg/kg N Y Y Y U J 7440360 7440428 7440097 7440235 7440382 0.625 1.1 2770 99.7 2.7 mg/kg mg/kg mg/kg mg/kg mg/kg 1.1 5.52 2770 99.7 2.7 mg/kg mg/kg mg/kg mg/kg mg/kg N N Y Y Y UJ UJ Validation Note U F U J F B J J J U U U U U U U U U UJ U U U U U U U U U U UJ U UJ U U U U U Q, Q B B L B Q Q, Q Q, Q, B, Original Result = 5.8 F F Q, Q Q, Q F, RL changed from 1.13 and  MDL from 0.338 $ F, RL changed from 2.25 and  MDL from 0.743 I,$ MDL and result changed  from 0.342 I Boeing Soil Char Level  (mg/kg) 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 Exceeds Boeing Soil Char Level No No No Yes No Yes No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No Ratio Boeing Soil Char Level 1.72E‐01 4.20E‐01 4.05E‐01 2.54E+00 4.40E‐01 2.15E+00 2.53E‐01 3.10E‐01 2.48E‐01 1.77E‐01 3.43E‐01 2.50E‐01 3.03E‐02 3.81E‐01 3.79E‐02 4.60E‐04 2.09E‐01 3.21E‐04 7.32E‐07 6.25E‐03 2.09E‐05 3.38E‐03 9.52E‐04 6.67E‐04 No SL 4.60E‐04 No SL 5.81E‐04 4.70E‐02 1.73E‐02 1.38E‐05 6.90E‐03 4.10E‐03 5.63E‐04 7.83E‐05 No SL 1.35E‐03 No SL 4.60E+00 4.00E‐04 1.02E‐03 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ ‐‐ No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No SL 2.00E‐04 1.57E‐02 1.84E‐04 No SL 9.23E‐03 2.00E‐04 1.44E‐03 1.30E‐02 8.57E‐05 No SL 2.46E‐03 1.44E‐03 No SL 1.95E‐04 No SL 1.38E‐03 2.47E‐04 4.13E‐05 1.12E‐04 7.79E‐04 1.13E‐06 No SL 1.55E‐03 5.45E‐04 7.54E‐05 2.47E‐05 2.88E‐04 5.29E‐04 2.88E‐04 4.86E‐04 4.69E‐03 No SL 8.57E‐06 4.18E‐03 4.33E‐03 3.05E‐05 2.11E‐05 No SL 2.26E‐03 2.71E‐05 8.82E‐02 6.50E‐04 No SL No SL 35 2340 ‐‐ No No No SL 863.2 ‐‐ ‐‐ 37900 No No SL No SL No 0.5 22 7524 754 24.2 Yes No No No No SCL Basis Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL SCL Units RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 130 1.1 5.5 27 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 4.6 4.6 0.92 1.8 1.8 4.6 1.8 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.6 46 9.2 4.6 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 65 0.68 1.1 0.75 0.014 0.016 0.0067 0.089 0.055 0.018 0.044 0.088 0.0049 0.0033 0.0061 0.41 0.54 0.66 0.51 0.64 0.42 0.83 0.54 0.64 0.55 0.52 0.71 0.59 0.54 0.54 0.52 0.65 0.55 0.58 0.59 0.54 0.66 0.57 4.6 1.6 0.97 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 9.2 1.8 4.6 4.6 1.8 4.6 4.6 0.92 1.8 4.6 1.8 4.6 4.6 1.8 1.8 1.8 1.8 0.92 4.6 1.8 9.2 4.6 4.6 1.8 4.6 1.8 4.6 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 1.8 4.6 1.8 2.21 2.25 2.25 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 3.5 0.5 0.56 0.57 0.5 0.5 0.51 0.46 0.62 0.65 0.59 0.41 0.8 0.61 0.26 0.6 0.65 0.42 0.34 0.75 1.8 1.2 0.81 1.2 0.55 0.47 0.56 0.69 0.73 0.5 0.48 0.42 0.62 0.53 0.74 0.66 0.41 0.43 0.55 0.44 0.29 0.276 0.743 0.743 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 7.94E‐02 Ecological RBSL 6.58E‐04 Ecological RBSL No SL mg/kg mg/kg mg/kg 2.78 mg/kg 1.13 mg/kg 1.13 mg/kg 2.78 mg/kg 0.338 mg/kg 0.338 mg/kg Y Y Y Y Y Y Y Y Y 4.01E‐03 Background No SL No SL 2.47E‐01 Background mg/kg mg/kg ph Units mg/kg 3.46 4.5 0.1 22.1 mg/kg mg/kg pH Units mg/kg mg/kg mg/kg pH Units mg/kg Y Y Y Y Y Y Y Y Y Y Y Y 2.20E+00 2.51E‐01 3.68E‐01 1.32E‐01 1.12E‐01 mg/kg mg/kg mg/kg mg/kg mg/kg 1.1 5.52 16.6 16.6 1.1 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Background Background Background 3.46 1.13 0.01 7.51 0.625 1.1 5.52 4.97 0.329 Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S010 ELBS1015S060 ELBS1015S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:00 4/8/08 9:10 4/8/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum 7440280 7440622 7440666 7440677 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 0.25 35.1 40.3 2.6 0.01 1.1 1.1 1.1 1.1 1.1 5.52 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 5.52 5.52 1.1 5.52 1.1 5.52 5.52 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 2.21 5.52 1.1 1.1 1.1 1.1 1.1 1.1 0.234 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 2.48 10800 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 0.577 1.07 1420 105 3.2 106 0.58 0.094 19.2 4.8 6.4 4.4 20.4 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg EEL EEL CC 1 Soil Boring ELBS1015 ELBS1015S060 Primary Sample 4/8/08 9:10 Soil 5 6 In Place Primary Result Metals 6020 Molybdenum 7439987 0.107 mg/kg RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Result  Value  Units In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 99.7 0.54 0.26 15.9 6.1 10.4 6.1 12.8 0.5 11.4 0.549 0.0439 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Page 16 of 108 Result  in SL Units 99.7 0.54 0.26 15.9 6.1 10.4 6.1 12.8 0.5 11.4 1.1 0.22 SL Units Detected mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y N N 0.25 mg/kg 35.1 mg/kg 40.3 mg/kg 2.6 mg/kg 0.01 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.00552 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.00552 mg/kg 0.00552 mg/kg 0.0011 mg/kg 0.00552 mg/kg 0.0011 mg/kg 0.00552 mg/kg 0.00552 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.00221 mg/kg 0.00552 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.000234 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.00248 mg/kg 10800 mg/kg N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N Y 1.07 5.37 1420 105 3.2 106 0.58 0.094 19.2 4.8 6.4 4.4 20.4 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y Y Y Y Y Y Y Y Y Y Y 0.107 mg/kg N Project  Qual  Code Validation Note U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U UJ UJ F, RL changed from 0.22 and  MDL from 0.0439 B, B, B, B I,$ MDL and result changed  from 0.333 I J U B, result changed from 0.069  and MDL from 0.0214 Boeing Soil Char Level  (mg/kg) 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 Exceeds Boeing Soil Char Level No No No No No No No No No No Yes No Ratio Boeing Soil Char Level 4.89E‐01 1.13E‐01 5.98E‐01 2.65E‐01 2.33E‐01 2.48E‐01 1.80E‐01 1.99E‐01 3.05E‐01 1.78E‐01 1.10E+00 2.22E‐01 0.761 111.8 153 10.64 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No 3.29E‐01 3.14E‐01 2.63E‐01 2.44E‐01 1.15E‐02 1.10E‐04 5.00E‐02 3.83E‐04 4.47E‐07 3.82E‐03 2.51E‐05 2.06E‐03 5.82E‐04 1.59E‐04 No SL 1.10E‐04 No SL 3.55E‐04 1.12E‐02 1.06E‐02 8.46E‐06 4.21E‐03 2.51E‐03 3.44E‐04 4.78E‐05 No SL 8.27E‐04 No SL 6.76E‐07 5.52E‐01 6.88E‐05 2.40E‐04 6.88E‐05 1.23E‐03 1.20E‐04 9.57E‐03 4.40E‐05 No SL 5.64E‐03 4.78E‐05 3.44E‐04 1.55E‐02 5.24E‐05 No SL 1.50E‐03 3.44E‐04 1.19E‐04 No SL 1.51E‐04 4.93E‐05 2.68E‐05 4.76E‐04 8.46E‐04 6.70E‐04 1.86E‐03 No SL 1.80E‐05 1.51E‐05 3.24E‐04 2.97E‐04 1.12E‐03 1.11E‐06 1.00E‐03 2.64E‐03 1.86E‐05 1.29E‐05 No SL 1.38E‐03 6.47E‐06 5.39E‐02 7.29E‐04 2.85E‐01 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 Yes No No No No No No No No No No No No 2.14E+00 2.44E‐01 1.89E‐01 1.39E‐01 1.32E‐01 5.20E‐01 1.21E‐01 2.16E‐01 3.19E‐01 1.83E‐01 1.52E‐01 1.30E‐01 3.17E‐01 1.642 No 6.52E‐02 Background SCL Basis SCL Units RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA Background Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.439 0.11 0.22 0.659 0.22 0.22 0.439 2.2 0.11 0.439 1.1 0.22 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.11 0.022 0.022 0.22 0.022 0.0439 0.11 0.439 0.022 0.11 0.549 0.0439 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.25 11 2.2 0.439 0.0115 1.1 1.1 1.1 1.1 1.1 5.52 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 5.52 5.52 1.1 5.52 1.1 5.52 5.52 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 2.21 5.52 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 2.48 21.5 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.25 2.2 0.439 0.11 0.00172 0.331 0.552 0.221 0.331 0.276 1.1 0.331 0.331 0.331 0.276 0.276 0.552 0.221 0.552 0.221 0.221 0.276 0.331 0.221 0.221 0.331 0.221 0.331 1.88 1.38 0.221 1.68 0.265 1.2 2.85 0.364 0.221 0.552 0.221 0.331 0.552 0.221 0.221 0.552 0.221 0.552 0.331 0.221 0.331 0.331 0.552 0.221 0.221 0.276 2.21 0.221 0.221 0.221 0.221 0.276 0.221 0.221 0.221 0.221 0.32 0.331 0.331 0.276 0.552 0.552 0.31 7.3 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.07 5.37 16.1 16.1 1.07 0.428 0.107 0.214 0.642 0.214 0.214 0.428 2.14 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.577 1.07 5.37 4.83 0.321 0.107 0.0214 0.0214 0.214 0.0214 0.0428 0.107 0.428 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y N N N N Y N Y N Y N N N mg/kg 0.107 mg/kg Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL 0.107 mg/kg Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015S060 ELBS1015S060 ELBS1015S060 Primary Sample Primary Sample Primary Sample 4/8/08 9:10 Soil 4/8/08 9:10 Soil 4/8/08 9:10 Soil Sample  Bottom  Depth (feet bgs) 5 6 5 6 5 6 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 Sample ID Sample Type Collection  Date Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place Primary Result Primary Result Primary Result Metals Metals Metals 6020 6020 6020 Nickel Selenium Silver 7440020 7782492 7440224 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum Barium Beryllium Boron Cobalt Copper Lithium Molybdenum Potassium Silver Sodium Vanadium Zinc Zirconium Arsenic Cadmium Chromium Lead Nickel Selenium Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 7440280 7440622 7440666 7440677 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 7440393 7440417 7440428 7440484 7440508 7439932 7439987 7440097 7440224 7440235 7440622 7440666 7440677 7440382 7440439 7440473 7439921 7440020 7782492 7440280 7439976 120821 87683 630206 71556 Page 17 of 108 Result  Value Result  Value  Units 10.8 mg/kg 0.535 mg/kg 0.066 mg/kg 0.23 26.9 45.4 2.2 0.0066 1.24 1.24 1.24 1.24 1.24 6.19 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 6.19 6.19 1.24 6.19 1.24 6.19 6.19 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 2.48 6.19 1.24 1.24 1.24 1.24 1.24 1.24 0.464 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 5 17000 100 0.715 6.65 4.03 7.82 26.7 0.282 1960 0.248 116 27.8 47.5 3.64 5.6 0.0715 25.2 6.53 16 0.514 0.253 0.0115 5 5 5 5 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units Detected 10.8 mg/kg 1.07 mg/kg 0.066 mg/kg Y N Y 0.23 mg/kg 26.9 mg/kg 45.4 mg/kg 2.2 mg/kg 0.0066 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00619 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00619 mg/kg 0.00619 mg/kg 0.00124 mg/kg 0.00619 mg/kg 0.00124 mg/kg 0.00619 mg/kg 0.00619 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00248 mg/kg 0.00619 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.000464 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.00124 mg/kg 0.005 mg/kg 17000 mg/kg 100 mg/kg 0.715 mg/kg 5.64 mg/kg 4.03 mg/kg 7.82 mg/kg 26.7 mg/kg 1.13 mg/kg 1960 mg/kg 0.564 mg/kg 116 mg/kg 27.8 mg/kg 47.5 mg/kg 3.64 mg/kg 5.6 mg/kg 0.0715 mg/kg 25.2 mg/kg 6.53 mg/kg 16 mg/kg 1.11 mg/kg 0.276 mg/kg 0.108 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N Y Y Y N Y Y Y N Y N Y Y Y Y Y Y Y Y Y N N N N N N N Project  Qual  Code Validation Note U J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U J U F, RL changed from 0.214 and  MDL from 0.0428 B, B, B, B T, result changed from 2.64 Q, Q B B B B, B U U Q, Q, B B J Q J B, Q Q, Q Q, Q U U UJ U U U U Q, F B,H Boeing Soil Char Level  (mg/kg) 64.2 1 0.99 Exceeds Boeing Soil Char Level No Yes No 0.761 111.8 153 10.64 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 203.8 4.8 22 26.18 42 64.4 1.642 7524 0.99 754 111.8 153 10.64 24.2 0.435 60.11 33.9 64.2 1 0.761 0.87 10 0.022 2.87 2460 No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No No Ratio Boeing SCL Basis Soil Char Level 1.68E‐01 Background 1.07E+00 MRL 6.67E‐02 Ecological RBSL mg/kg mg/kg mg/kg 3.02E‐01 2.41E‐01 2.97E‐01 2.07E‐01 7.59E‐03 1.24E‐04 5.64E‐02 4.32E‐04 5.04E‐07 4.31E‐03 2.81E‐05 2.33E‐03 6.56E‐04 1.80E‐04 No SL 1.24E‐04 No SL 4.00E‐04 1.27E‐02 1.19E‐02 9.54E‐06 4.75E‐03 2.82E‐03 3.88E‐04 5.39E‐05 No SL 9.32E‐04 No SL 7.59E‐07 6.19E‐01 7.75E‐05 2.69E‐04 7.75E‐05 1.38E‐03 1.35E‐04 1.08E‐02 4.96E‐05 No SL 6.36E‐03 5.39E‐05 3.88E‐04 1.75E‐02 5.90E‐05 No SL 1.69E‐03 3.88E‐04 1.34E‐04 No SL 1.70E‐04 5.56E‐05 3.02E‐05 5.37E‐04 9.54E‐04 7.52E‐04 2.08E‐03 No SL 2.03E‐05 1.70E‐05 3.65E‐04 3.35E‐04 1.27E‐03 2.21E‐06 1.13E‐03 2.98E‐03 2.10E‐05 1.45E‐05 No SL 1.56E‐03 7.29E‐06 6.08E‐02 1.47E‐03 4.49E‐01 4.91E‐01 1.49E‐01 2.56E‐01 1.54E‐01 1.86E‐01 4.15E‐01 6.88E‐01 2.60E‐01 5.70E‐01 1.54E‐01 2.49E‐01 3.10E‐01 3.42E‐01 2.31E‐01 1.64E‐01 4.19E‐01 1.93E‐01 2.49E‐01 1.11E+00 3.63E‐01 1.24E‐01 5.00E‐04 2.27E‐01 1.74E‐03 2.03E‐06 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units RL RL Units 0.428 mg/kg 1.07 mg/kg 0.214 mg/kg 0.23 10.7 2.14 0.428 0.0111 1.24 1.24 1.24 1.24 1.24 6.19 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 6.19 6.19 1.24 6.19 1.24 6.19 6.19 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 2.48 6.19 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 5 22.5 0.564 0.564 5.64 0.564 1.13 0.56 1.13 56.4 0.564 113 0.564 2.25 5.64 1.11 0.138 1.11 0.553 1.11 1.11 0.276 0.108 5 5 5 5 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg MDL MDL  Units 0.107 mg/kg 0.535 mg/kg 0.0428 mg/kg 0.23 2.14 0.428 0.107 0.00166 0.371 0.619 0.248 0.371 0.31 1.24 0.371 0.371 0.371 0.31 0.31 0.619 0.248 0.619 0.248 0.248 0.31 0.371 0.248 0.248 0.371 0.248 0.371 2.1 1.55 0.248 1.88 0.297 1.35 3.19 0.409 0.248 0.619 0.248 0.371 0.619 0.248 0.248 0.619 0.248 0.619 0.371 0.248 0.371 0.371 0.619 0.248 0.248 0.31 2.48 0.248 0.248 0.248 0.248 0.31 0.248 0.248 0.248 0.248 0.359 0.371 0.371 0.31 0.619 0.619 1 3.78 0.0259 0.0767 0.699 0.147 0.225 0.11 0.282 3.73 0.192 39.2 0.18 0.738 1.13 0.111 0.0531 0.332 0.0829 0.315 0.514 0.0829 0.0115 1 2 1 1 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N Y Y N Y Y N Y N Y Y Y Y Y N Y Y Y Y N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1015 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1015X060 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 ELBS1015S060 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 4/8/08 9:10 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9045C 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Bromide Chloride Fluoride Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane Page 18 of 108 CAS Number 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 24959679 16887006 16984488 NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 Result  Value 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 16 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5.4 8.8 0.43 5.6 2.2 0.61 1 7 12000 93 0.88 1.4 16 4.9 15 2800 87 32 41 2.3 0.28 5.3 0.17 9.5 9 0.47 11 0.31 0.064 0.22 0.013 5.4 5.4 1.1 2.2 2.2 5.4 2.2 2.2 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.01 0.016 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.0054 8.8 5.5 5.5 2.2 0.61 1 7 12000 93 0.88 1.4 16 4.9 15 2800 130 32 41 2.3 0.28 5.3 0.17 9.5 9 0.47 11 0.31 0.064 0.22 0.013 0.0054 0.0054 0.0011 0.0022 0.0022 0.0054 0.0022 0.0022 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U J U U U U U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J J J Validation Note Q Q Q Q Q L F Q Q Q Q Q B H H Q, Q J B U F J J B J J J J U U U U U U U U Q, Q B B Boeing Soil Char Level  (mg/kg) 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ ‐‐ ‐‐ 35 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 Exceeds Boeing Soil Char Level No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No SL No SL No No SL No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 1.74E‐02 4.55E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 4.35E‐04 2.22E‐03 3.48E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 3.85E‐03 6.87E‐04 2.24E‐04 1.22E‐04 2.16E‐03 1.23E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 1.59E‐03 No SL No SL No SL 6.29E‐02 No SL 1.16E‐03 No SL 3.17E‐01 4.56E‐01 1.83E‐01 6.36E‐02 2.66E‐01 1.87E‐01 2.33E‐01 3.72E‐01 1.72E‐01 2.86E‐01 2.68E‐01 2.16E‐01 5.60E‐01 2.19E‐01 3.91E‐01 2.26E‐01 2.65E‐01 2.86E‐01 1.71E‐01 3.10E‐01 6.46E‐02 2.89E‐01 1.49E‐02 5.40E‐04 2.45E‐01 3.83E‐04 8.94E‐07 7.64E‐03 2.45E‐05 4.13E‐03 1.16E‐03 SCL Basis Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 20 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5.4 0.1 5.5 5.5 5.5 5.5 5.5 5.5 11 0.55 0.33 5.5 1.1 0.55 7 110 130 1.1 5.5 28 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 5.4 5.4 1.1 2.2 2.2 5.4 2.2 2.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL MDL  Units 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 3 3 7 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 1 2 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1.4 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.43 2.2 0.91 0.37 0.56 1.9 5.4 0.27 0.17 1.1 0.44 0.11 0.33 45 65 0.69 1.1 0.75 0.014 0.016 0.0068 0.09 0.055 0.018 0.044 0.089 0.0049 0.0033 0.0061 0.47 0.62 0.76 0.59 0.74 0.48 0.97 0.62 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N Y N N Y N N N N N N N N N N N Y N N N N N N N N N Y N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S010 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:40 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane Page 19 of 108 CAS Number 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 Result  Value 5.4 2.2 5.4 1.1 2.2 5.4 2.2 2.2 2.2 2.2 2.2 2.2 2.2 2.2 5.4 54 11 5.4 11 2.2 5.4 5.4 2.2 5.4 5.4 1.1 2.2 5.4 2.2 5.4 5.4 2.2 2.2 2.2 2.2 1.1 5.4 2.2 11 5.4 5.4 5.4 5.4 2.2 5.4 5.4 5.4 2.2 5.4 1.1 2.2 5.4 2.2 2.2 2.2 2.2 2.2 5.4 2.2 1.8 21000 230 1.9 1.1 27 9.5 58 2700 220 58 91 1.1 0.26 21 0.14 17 12 0.35 28 0.51 0.07 0.38 0.0083 4.6 4.6 0.92 1.8 1.8 4.6 1.8 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0054 0.0022 0.0054 0.0011 0.0022 0.0054 0.0022 0.0022 0.0022 0.0022 0.0022 0.0022 0.0022 0.0022 0.0054 0.054 0.011 0.0054 0.011 0.0022 0.0054 0.0054 0.0022 0.0054 0.0054 0.0011 0.0022 0.0054 0.0022 0.0054 0.0054 0.0022 0.0022 0.0022 0.0022 0.0011 0.0054 0.0022 0.011 0.0054 0.0054 0.0054 0.0054 0.0022 0.0054 0.0054 0.0054 0.0022 0.0054 0.0011 0.0022 0.0054 0.0022 0.0022 0.0022 0.0022 0.0022 0.0054 0.0022 0.0018 21000 230 1.9 5.7 27 9.5 58 2700 220 58 91 28 0.26 21 0.14 17 12 0.35 28 0.51 0.07 0.38 0.0083 0.0046 0.0046 0.00092 0.0018 0.0018 0.0046 0.0018 0.0018 0.0046 0.0018 0.0046 0.00092 0.0018 0.0046 0.0018 0.0018 0.0018 0.0018 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N Project  Qual  Code UJ U U U U U U U U U U UJ U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U Validation Note L B Q Q, Q Q, Q, B F F Q, Q Q, Q Q, Q U B U J F B J J J J U U U U U U U U UJ U U U U U U U U U Q, Q B B L B Boeing Soil Char Level  (mg/kg) 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 Exceeds Boeing Soil Char Level No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No Yes No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No Ratio Boeing Soil Char Level 7.83E‐04 No SL 5.40E‐04 No SL 7.10E‐04 5.52E‐02 2.12E‐02 1.69E‐05 8.43E‐03 5.01E‐03 6.88E‐04 9.57E‐05 No SL 1.65E‐03 No SL 5.40E+00 4.78E‐04 1.20E‐03 2.39E‐04 1.91E‐02 2.16E‐04 No SL 1.13E‐02 2.35E‐04 1.69E‐03 1.55E‐02 1.05E‐04 No SL 3.00E‐03 1.69E‐03 No SL 2.39E‐04 No SL 1.69E‐03 3.02E‐04 4.93E‐05 1.32E‐04 9.52E‐04 1.35E‐06 No SL 1.82E‐03 1.64E‐03 8.85E‐05 3.01E‐05 3.38E‐04 1.59E‐03 3.38E‐04 5.95E‐04 5.51E‐03 No SL 1.05E‐05 4.91E‐03 5.29E‐03 3.73E‐05 2.58E‐05 No SL 2.76E‐03 3.18E‐05 1.08E‐01 5.29E‐04 5.54E‐01 1.13E+00 3.96E‐01 2.59E‐01 4.49E‐01 3.63E‐01 9.01E‐01 3.59E‐01 2.92E‐01 5.19E‐01 5.95E‐01 2.63E+00 5.20E‐01 8.68E‐01 3.22E‐01 4.05E‐01 3.54E‐01 2.13E‐01 4.36E‐01 5.10E‐01 7.07E‐02 4.99E‐01 9.54E‐03 4.60E‐04 2.09E‐01 3.21E‐04 7.32E‐07 6.25E‐03 2.09E‐05 3.38E‐03 9.52E‐04 6.67E‐04 No SL 4.60E‐04 No SL 5.81E‐04 4.70E‐02 1.73E‐02 1.38E‐05 6.90E‐03 4.10E‐03 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.4 2.2 5.4 1.1 2.2 5.4 2.2 2.2 2.2 2.2 2.2 2.2 2.2 2.2 5.4 54 11 5.4 11 2.2 5.4 5.4 2.2 5.4 5.4 1.1 2.2 5.4 2.2 5.4 5.4 2.2 2.2 2.2 2.2 1.1 5.4 2.2 11 5.4 5.4 5.4 5.4 2.2 5.4 5.4 5.4 2.2 5.4 1.1 2.2 5.4 2.2 2.2 2.2 2.2 2.2 5.4 2.2 1.8 11 0.57 0.34 5.7 1.1 0.57 7.2 110 140 1.1 5.7 28 1.1 0.57 0.23 0.23 0.46 0.11 0.46 1.1 0.23 0.23 0.034 4.6 4.6 0.92 1.8 1.8 4.6 1.8 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.74 0.65 0.6 0.83 0.69 0.62 0.63 0.6 0.75 0.65 0.68 0.69 0.63 0.76 0.67 5.4 1.9 1.1 4.1 0.58 0.66 0.67 0.58 0.58 0.59 0.54 0.72 0.75 0.69 0.47 0.94 0.71 0.3 0.7 0.75 0.49 0.4 0.87 2.1 1.4 0.95 1.4 0.65 0.55 0.66 0.81 0.85 0.58 0.56 0.48 0.72 0.61 0.86 0.77 0.47 0.51 0.65 0.52 0.33 1.2 5.6 0.27 0.17 1.1 0.46 0.11 0.34 47 67 0.71 1.1 0.77 0.014 0.017 0.007 0.092 0.057 0.018 0.046 0.091 0.005 0.0034 0.0063 0.41 0.54 0.66 0.51 0.64 0.42 0.83 0.54 0.64 0.55 0.52 0.71 0.59 0.54 0.54 0.52 0.65 0.55 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1016 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1016S060 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:50 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) 108678 541731 142289 106467 75887 110758 591786 108101 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9045C 9056 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Bromide Chloride Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 24959679 16887006 16984488 NO3N NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 Page 20 of 108 Result  Value 1.8 1.8 1.8 1.8 4.6 46 9.2 4.6 9.2 1.8 4.6 4.6 1.8 4.6 4.6 0.92 1.8 4.6 1.8 4.6 4.6 1.8 1.8 1.8 1.8 0.92 4.6 1.8 9.2 4.6 4.6 1.8 4.6 1.8 4.6 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 1.8 4.6 1.8 1.9 6.4 0.4 5.5 1.7 3.3 0.56 0.8 20 7400 110 0.7 1 8 5.3 11 3700 160 29 36 0.78 0.096 1.3 0.04 11 2.9 0.33 6.6 0.15 0.035 0.16 0.0074 4.9 4.9 0.97 1.9 1.9 4.9 1.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0018 0.0018 0.0018 0.0018 0.0046 0.046 0.0092 0.0046 0.0092 0.0018 0.0046 0.0046 0.0018 0.0046 0.0046 0.00092 0.0018 0.0046 0.0018 0.0046 0.0046 0.0018 0.0018 0.0018 0.0018 0.00092 0.0046 0.0018 0.0092 0.0046 0.0046 0.0018 0.0046 0.0018 0.0046 0.0018 0.0046 0.0018 0.0046 0.00092 0.0018 0.0046 0.0018 0.0018 0.0018 0.0018 0.0018 0.0046 0.0018 0.0019 6.4 5.1 5.1 1.7 3.3 0.56 0.8 20 7400 110 0.7 5.1 8 5.3 11 3700 160 29 36 26 1 1.3 0.04 11 2.9 0.33 6.6 0.15 0.035 0.16 0.0074 0.0049 0.0049 0.00097 0.0019 0.0019 0.0049 0.0019 0.0019 0.0049 0.0019 0.0049 0.00097 0.0019 0.0049 0.0019 0.0019 0.0019 0.0019 0.0019 Detected Project  Qual  Code mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N U UJ U UJ U U U U mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y N N Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U SL Units U U J J J J Validation Note Q Q, Q Q, Q, B, Original Result = 5.2 F F Q, Q Q, Q B H H H Q, Q U B U U F B J J J J J U U U U U U U U UJ U U U U U U U U U U Q, Q B B L B Boeing Soil Char Level  (mg/kg) 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 Exceeds Boeing Soil Char Level No No No SL No No SL Yes No No Ratio Boeing Soil Char Level 5.63E‐04 7.83E‐05 No SL 1.35E‐03 No SL 4.60E+00 4.00E‐04 1.02E‐03 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No SL No SL No No No SL No No SL No No No No No No No No No No No Yes Yes No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No 2.00E‐04 1.57E‐02 1.84E‐04 No SL 9.23E‐03 2.00E‐04 1.44E‐03 1.30E‐02 8.57E‐05 No SL 2.46E‐03 1.44E‐03 No SL 1.95E‐04 No SL 1.38E‐03 2.47E‐04 4.13E‐05 1.12E‐04 7.79E‐04 1.13E‐06 No SL 1.55E‐03 5.45E‐04 7.54E‐05 2.47E‐05 2.88E‐04 5.29E‐04 2.88E‐04 4.86E‐04 4.69E‐03 No SL 8.57E‐06 4.18E‐03 4.33E‐03 3.05E‐05 2.11E‐05 No SL 2.26E‐03 2.71E‐05 8.82E‐02 5.59E‐04 No SL No SL No SL 4.86E‐02 1.41E‐03 No SL 9.27E‐04 No SL 1.95E‐01 5.40E‐01 1.46E‐01 2.32E‐01 1.33E‐01 2.02E‐01 1.71E‐01 4.92E‐01 2.12E‐01 2.59E‐01 2.35E‐01 2.44E+00 2.00E+00 5.37E‐02 9.20E‐02 2.62E‐01 8.55E‐02 2.01E‐01 1.03E‐01 1.50E‐01 3.54E‐02 2.10E‐01 8.51E‐03 4.90E‐04 2.23E‐01 3.38E‐04 7.72E‐07 6.60E‐03 2.23E‐05 3.56E‐03 1.01E‐03 7.10E‐04 No SL 4.90E‐04 No SL 6.13E‐04 5.01E‐02 1.83E‐02 1.46E‐05 7.28E‐03 4.33E‐03 5.94E‐04 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.8 1.8 1.8 1.8 4.6 46 9.2 4.6 9.2 1.8 4.6 4.6 1.8 4.6 4.6 0.92 1.8 4.6 1.8 4.6 4.6 1.8 1.8 1.8 1.8 0.92 4.6 1.8 9.2 4.6 4.6 1.8 4.6 1.8 4.6 1.8 4.6 1.8 4.6 0.92 1.8 4.6 1.8 1.8 1.8 1.8 1.8 4.6 1.8 1.9 0.1 5.1 5.1 5.1 5.1 5.1 5.1 5.1 10 0.51 0.31 5.1 1 0.51 6.5 100 120 1 5.1 26 1 0.51 0.21 0.21 0.41 0.1 0.41 1 0.21 0.21 0.031 4.9 4.9 0.97 1.9 1.9 4.9 1.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.58 0.59 0.54 0.66 0.57 4.6 1.6 0.97 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.5 0.5 0.56 0.57 0.5 0.5 0.51 0.46 0.62 0.65 0.59 0.41 0.8 0.61 0.26 0.6 0.65 0.42 0.34 0.75 1.8 1.2 0.81 1.2 0.55 0.47 0.56 0.69 0.73 0.5 0.48 0.42 0.62 0.53 0.74 0.66 0.41 0.43 0.55 0.44 0.29 1.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.4 2 0.84 0.32 0.34 0.51 1.8 5 0.25 0.15 1 0.41 0.1 0.31 42 60 0.64 1 0.7 0.013 0.015 0.0063 0.083 0.051 0.016 0.041 0.082 0.0045 0.0031 0.0057 0.43 0.56 0.69 0.54 0.67 0.44 0.88 0.56 0.67 0.58 0.55 0.75 0.62 0.56 0.57 0.55 0.68 0.58 0.61 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S010 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:00 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Page 21 of 108 CAS Number 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 Result  Value 1.9 1.9 1.9 4.9 49 9.7 4.9 9.7 1.9 4.9 4.9 1.9 4.9 4.9 0.97 1.9 4.9 1.9 4.9 4.9 1.9 1.9 1.9 1.9 0.97 4.9 1.9 9.7 4.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 4.9 1.9 1.9 12000 86 0.75 1.1 17 3.1 23 1400 90 32 31 1.4 0.21 8.4 0.12 6.4 4.5 0.2 13 0.3 0.083 0.16 0.0061 4.7 4.7 0.95 1.9 1.9 4.7 1.9 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.7 47 9.5 4.7 9.5 1.9 4.7 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0019 0.0019 0.0019 0.0049 0.049 0.0097 0.0049 0.0097 0.0019 0.0049 0.0049 0.0019 0.0049 0.0049 0.00097 0.0019 0.0049 0.0019 0.0049 0.0049 0.0019 0.0019 0.0019 0.0019 0.00097 0.0049 0.0019 0.0097 0.0049 0.0049 0.0019 0.0049 0.0019 0.0049 0.0019 0.0049 0.0019 0.0049 0.00097 0.0019 0.0049 0.0019 0.0019 0.0019 0.0019 0.0019 0.0049 0.0019 0.0019 12000 86 0.75 5.5 17 3.1 23 1400 130 32 31 28 0.21 8.4 0.12 6.4 4.5 0.2 13 0.3 0.083 0.16 0.033 0.0047 0.0047 0.00095 0.0019 0.0019 0.0047 0.0019 0.0019 0.0047 0.0019 0.0047 0.00095 0.0019 0.0047 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0047 0.047 0.0095 0.0047 0.0095 0.0019 0.0047 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code UJ U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U Validation Note Q Q, Q Q, Q, B, Original Result = 4 F F Q, Q Q, Q Q, Q U B U F U J F B J J J J U U U U U U U U U UJ U U U U U U U U U U UJ U UJ U U U U U U U Q, Q B B L B Q Q, Q Q, Q, B Boeing Soil Char Level  (mg/kg) 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 Exceeds Boeing Soil Char Level No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No Ratio Boeing Soil Char Level 8.26E‐05 No SL 1.43E‐03 No SL 4.90E+00 4.22E‐04 1.09E‐03 2.11E‐04 1.65E‐02 1.96E‐04 No SL 9.74E‐03 2.13E‐04 1.53E‐03 1.37E‐02 9.05E‐05 No SL 2.59E‐03 1.53E‐03 No SL 2.06E‐04 No SL 1.46E‐03 2.61E‐04 4.35E‐05 1.20E‐04 8.23E‐04 1.19E‐06 No SL 1.65E‐03 5.76E‐04 8.03E‐05 2.60E‐05 3.06E‐04 5.59E‐04 3.06E‐04 5.14E‐04 5.00E‐03 No SL 9.05E‐06 4.45E‐03 4.57E‐03 3.22E‐05 2.23E‐05 No SL 2.38E‐03 2.88E‐05 9.31E‐02 5.59E‐04 3.17E‐01 4.22E‐01 1.56E‐01 2.50E‐01 2.83E‐01 1.18E‐01 3.57E‐01 1.86E‐01 1.72E‐01 2.86E‐01 2.03E‐01 2.63E+00 4.20E‐01 3.47E‐01 2.76E‐01 1.52E‐01 1.33E‐01 1.22E‐01 2.02E‐01 3.00E‐01 8.38E‐02 2.10E‐01 3.79E‐02 4.70E‐04 2.14E‐01 3.31E‐04 7.72E‐07 6.60E‐03 2.14E‐05 3.56E‐03 1.01E‐03 6.81E‐04 No SL 4.70E‐04 No SL 6.13E‐04 4.81E‐02 1.83E‐02 1.46E‐05 7.28E‐03 4.33E‐03 5.94E‐04 8.26E‐05 No SL 1.43E‐03 No SL 4.70E+00 4.13E‐04 1.04E‐03 2.07E‐04 1.65E‐02 1.88E‐04 SCL Basis Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 1.9 1.9 1.9 4.9 49 9.7 4.9 9.7 1.9 4.9 4.9 1.9 4.9 4.9 0.97 1.9 4.9 1.9 4.9 4.9 1.9 1.9 1.9 1.9 0.97 4.9 1.9 9.7 4.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 4.9 1.9 1.9 11 0.55 0.33 5.5 1.1 0.55 6.9 110 130 1.1 5.5 28 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 4.7 4.7 0.95 1.9 1.9 4.7 1.9 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.7 47 9.5 4.7 9.5 1.9 4.7 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.62 0.57 0.69 0.6 4.9 1.7 1 3.7 0.53 0.59 0.6 0.53 0.53 0.54 0.49 0.65 0.68 0.62 0.43 0.85 0.64 0.27 0.63 0.68 0.45 0.36 0.79 1.9 1.2 0.86 1.3 0.58 0.5 0.59 0.73 0.77 0.53 0.51 0.44 0.65 0.56 0.78 0.7 0.43 0.46 0.58 0.47 0.3 1.2 5.4 0.26 0.17 1.1 0.44 0.11 0.33 45 65 0.68 1.1 0.75 0.014 0.016 0.0067 0.089 0.055 0.018 0.044 0.088 0.0049 0.0033 0.0061 0.42 0.55 0.67 0.52 0.65 0.43 0.85 0.55 0.65 0.57 0.53 0.73 0.61 0.55 0.56 0.53 0.66 0.57 0.6 0.61 0.56 0.67 0.59 4.7 1.6 0.99 3.6 0.51 0.58 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/24/08 9:10 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 5.75 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1017 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1017S060 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9045C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 Page 22 of 108 Result  Value 4.7 1.9 4.7 4.7 0.95 1.9 4.7 1.9 4.7 4.7 1.9 1.9 1.9 1.9 0.95 4.7 1.9 9.5 4.7 4.7 1.9 4.7 1.9 4.7 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 4.7 1.9 1.8 8.6 13000 130 0.83 1.1 13 5.4 16 3400 130 50 46 1.8 1.2 100 0.11 7.5 5.5 0.41 10 0.26 0.087 0.21 0.014 4.5 4.5 0.9 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.9 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 9 4.5 9 1.8 4.5 4.5 1.8 4.5 4.5 0.9 1.8 4.5 1.8 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0047 0.0019 0.0047 0.0047 0.00095 0.0019 0.0047 0.0019 0.0047 0.0047 0.0019 0.0019 0.0019 0.0019 0.00095 0.0047 0.0019 0.0095 0.0047 0.0047 0.0019 0.0047 0.0019 0.0047 0.0019 0.0047 0.0019 0.0047 0.00095 0.0019 0.0047 0.0019 0.0019 0.0019 0.0019 0.0019 0.0047 0.0019 0.0018 8.6 13000 130 0.83 5.5 13 5.4 16 3400 130 50 46 1.8 1.2 100 0.11 7.5 5.5 0.41 10 0.26 0.087 0.21 0.014 0.0045 0.0045 0.0009 0.0018 0.0018 0.0045 0.0018 0.0018 0.0045 0.0018 0.0045 0.0009 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.045 0.009 0.0045 0.009 0.0018 0.0045 0.0045 0.0018 0.0045 0.0045 0.0009 0.0018 0.0045 0.0018 SL Units Detected Project  Qual  Code mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y N Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U UJ U U U U U UJ U U U U U U U U U U U mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ J Validation Note F F Q, Q Q, Q A U J A J A U J F, MDL changed from 65 A J J J A,Q J J J J J J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ Q Q Q $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H B,$,H, Result changed from  6.4 $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Boeing Soil Char Level  (mg/kg) ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 Exceeds Boeing Soil Char Level No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No No No No No No No No No No No No Yes Yes No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No Ratio Boeing Soil Char Level No SL 9.74E‐03 2.04E‐04 1.47E‐03 1.34E‐02 9.05E‐05 No SL 2.59E‐03 1.47E‐03 No SL 2.06E‐04 No SL 1.46E‐03 2.61E‐04 4.26E‐05 1.15E‐04 8.23E‐04 1.16E‐06 No SL 1.58E‐03 5.76E‐04 7.70E‐05 2.60E‐05 2.94E‐04 5.59E‐04 2.94E‐04 5.14E‐04 4.80E‐03 No SL 9.05E‐06 4.27E‐03 4.57E‐03 3.22E‐05 2.23E‐05 No SL 2.38E‐03 2.76E‐05 9.31E‐02 5.29E‐04 No SL 3.43E‐01 6.38E‐01 1.73E‐01 2.50E‐01 2.16E‐01 2.06E‐01 2.48E‐01 4.52E‐01 1.72E‐01 4.47E‐01 3.01E‐01 1.69E‐01 2.40E+00 4.13E+00 2.53E‐01 1.79E‐01 1.62E‐01 2.50E‐01 1.56E‐01 2.60E‐01 8.79E‐02 2.76E‐01 1.61E‐02 4.50E‐04 2.05E‐01 3.14E‐04 7.32E‐07 6.25E‐03 2.05E‐05 3.38E‐03 9.52E‐04 6.52E‐04 No SL 4.50E‐04 No SL 5.81E‐04 4.60E‐02 1.73E‐02 1.38E‐05 6.90E‐03 4.10E‐03 5.63E‐04 7.83E‐05 No SL 1.35E‐03 No SL 4.50E+00 3.91E‐04 1.00E‐03 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 No No No No SL No No No No No No SL No 1.96E‐04 1.57E‐02 1.80E‐04 No SL 9.23E‐03 1.96E‐04 1.41E‐03 1.27E‐02 8.57E‐05 No SL 2.46E‐03 SCL Basis Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 4.7 1.9 4.7 4.7 0.95 1.9 4.7 1.9 4.7 4.7 1.9 1.9 1.9 1.9 0.95 4.7 1.9 9.5 4.7 4.7 1.9 4.7 1.9 4.7 1.9 4.7 1.9 4.7 0.95 1.9 4.7 1.9 1.9 1.9 1.9 1.9 4.7 1.9 1.8 0.1 11 0.55 0.33 5.5 1.1 0.55 6.9 110 130 1.1 5.5 27 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 4.5 4.5 0.9 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.9 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 9 4.5 9 1.8 4.5 4.5 1.8 4.5 4.5 0.9 1.8 4.5 1.8 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL MDL  Units 0.59 0.51 0.51 0.52 0.47 0.63 0.66 0.61 0.42 0.82 0.63 0.27 0.62 0.66 0.44 0.35 0.77 1.8 1.2 0.83 1.2 0.57 0.48 0.58 0.71 0.75 0.51 0.49 0.43 0.63 0.54 0.76 0.68 0.42 0.45 0.57 0.45 0.29 1.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.4 0.26 0.16 1.1 0.44 0.11 0.33 45 130 0.68 1.1 0.75 0.014 0.016 0.0067 0.089 0.055 0.018 0.044 0.088 0.0049 0.0033 0.0061 0.4 0.52 0.64 0.5 0.62 0.41 0.81 0.52 0.62 0.54 0.5 0.69 0.58 0.52 0.53 0.5 0.63 0.54 0.57 0.58 0.53 0.64 0.56 4.5 1.6 0.95 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.4 0.49 0.55 0.56 0.49 0.49 0.5 0.45 0.6 0.63 0.58 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N N Y N Y Y Y Y N Y Y Y Y N N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018D010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 9045C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Analyte Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium CAS Number 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 E‐10139 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 Page 23 of 108 Result  Value 4.5 4.5 1.8 1.8 1.8 1.8 0.9 4.5 1.8 9 4.5 4.5 1.8 4.5 1.8 4.5 1.8 4.5 1.8 4.5 0.9 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 2 6.6 19000 91 1 1.3 20 4.7 19 1700 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 0.0045 0.0045 0.0018 0.0018 0.0018 0.0018 0.0009 0.0045 0.0018 0.009 0.0045 0.0045 0.0018 0.0045 0.0018 0.0045 0.0018 0.0045 0.0018 0.0045 0.0009 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.0018 0.002 6.6 19000 91 1 1.3 20 4.7 19 1700 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Project  Qual  Code Validation Note UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H J A J J A J A U J F, result changed from 100  and MDL from 68 A 140 37 36 2.5 0.26 3.7 0.064 6.4 6.1 0.45 12 0.3 0.065 0.25 0.0063 4.9 4.9 0.99 2 2 4.9 2 2 4.9 2 4.9 0.99 2 4.9 2 2 2 2 2 2 2 2 4.9 49 9.9 4.9 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 140 37 36 2.5 0.26 3.7 0.064 6.4 6.1 0.45 12 0.3 0.065 0.25 0.034 0.0049 0.0049 0.00099 0.002 0.002 0.0049 0.002 0.002 0.0049 0.002 0.0049 0.00099 0.002 0.0049 0.002 0.002 0.002 0.002 0.002 0.002 0.002 0.002 0.0049 0.049 0.0099 0.0049 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N U UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ 9.9 2 4.9 4.9 2 4.9 4.9 0.99 2 4.9 2 4.9 4.9 2 2 2 2 0.99 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0099 0.002 0.0049 0.0049 0.002 0.0049 0.0049 0.00099 0.002 0.0049 0.002 0.0049 0.0049 0.002 0.002 0.002 0.002 0.00099 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ J J J J J J J J A,Q Q Q Q $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H B,$,H, Result changed from  6.9 $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Boeing Soil Char Level  (mg/kg) 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 Exceeds Boeing Soil Char Level No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No SL No No No No No No No No Ratio Boeing Soil Char Level 1.41E‐03 No SL 1.95E‐04 No SL 1.38E‐03 2.47E‐04 4.04E‐05 1.10E‐04 7.79E‐04 1.10E‐06 No SL 1.52E‐03 5.45E‐04 7.38E‐05 2.47E‐05 2.81E‐04 5.29E‐04 2.81E‐04 4.86E‐04 4.59E‐03 No SL 8.57E‐06 4.09E‐03 4.33E‐03 3.05E‐05 2.11E‐05 No SL 2.26E‐03 2.65E‐05 8.82E‐02 5.88E‐04 No SL 5.01E‐01 4.47E‐01 2.08E‐01 5.91E‐02 3.33E‐01 1.80E‐01 2.95E‐01 2.26E‐01 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No 1.86E‐01 3.31E‐01 2.35E‐01 2.35E‐01 5.20E‐01 1.53E‐01 1.47E‐01 1.52E‐01 1.80E‐01 2.74E‐01 1.87E‐01 3.00E‐01 6.57E‐02 3.29E‐01 3.91E‐02 4.90E‐04 2.23E‐01 3.45E‐04 8.13E‐07 6.94E‐03 2.23E‐05 3.75E‐03 1.06E‐03 7.10E‐04 No SL 4.90E‐04 No SL 6.45E‐04 5.01E‐02 1.92E‐02 1.54E‐05 7.66E‐03 4.56E‐03 6.25E‐04 8.70E‐05 No SL 1.50E‐03 No SL 4.90E+00 4.30E‐04 1.09E‐03 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 No No No No SL No No No No No No SL No No No SL No No SL No No No 2.15E‐04 1.74E‐02 1.96E‐04 No SL 1.03E‐02 2.13E‐04 1.53E‐03 1.39E‐02 9.52E‐05 No SL 2.73E‐03 1.53E‐03 No SL 2.17E‐04 No SL 1.54E‐03 2.75E‐04 4.44E‐05 SCL Basis Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 4.5 4.5 1.8 1.8 1.8 1.8 0.9 4.5 1.8 9 4.5 4.5 1.8 4.5 1.8 4.5 1.8 4.5 1.8 4.5 0.9 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 2 0.1 11 0.57 0.34 5.7 1.1 0.57 7.2 110 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL MDL  Units 0.4 0.78 0.59 0.25 0.59 0.63 0.41 0.33 0.73 1.7 1.1 0.79 1.2 0.54 0.46 0.55 0.68 0.71 0.49 0.47 0.41 0.6 0.51 0.72 0.65 0.4 0.42 0.54 0.43 0.28 1.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.6 0.28 0.17 1.1 0.46 0.11 0.34 47 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 140 1.1 5.7 29 1.1 0.57 0.23 0.23 0.46 0.11 0.46 1.1 0.23 0.23 0.034 4.9 4.9 0.99 2 2 4.9 2 2 4.9 2 4.9 0.99 2 4.9 2 2 2 2 2 2 2 2 4.9 49 9.9 4.9 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 140 0.71 1.1 0.78 0.014 0.017 0.007 0.093 0.057 0.018 0.046 0.092 0.0051 0.0034 0.0063 0.43 0.57 0.7 0.54 0.68 0.44 0.89 0.57 0.68 0.59 0.55 0.76 0.63 0.57 0.58 0.55 0.69 0.59 0.62 0.63 0.58 0.7 0.61 4.9 1.7 1 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 9.9 2 4.9 4.9 2 4.9 4.9 0.99 2 4.9 2 4.9 4.9 2 2 2 2 0.99 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.8 0.53 0.6 0.61 0.53 0.53 0.54 0.49 0.66 0.69 0.63 0.43 0.86 0.65 0.28 0.64 0.69 0.45 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y Y Y N Y N N N N Y N N N N Y Y Y Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S010 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:40 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene Page 24 of 108 CAS Number 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 Result  Value 4.9 2 9.9 4.9 4.9 2 4.9 2 4.9 2 4.9 2 4.9 0.99 2 4.9 2 2 2 2 2 4.9 2 1.8 17000 79 1.1 1.1 19 4 24 1400 170 39 39 2.3 0.28 4.4 0.059 8.1 4.2 0.18 13 0.43 0.24 0.22 0.014 4.5 4.5 0.89 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 8.9 4.5 8.9 1.8 4.5 4.5 1.8 4.5 4.5 0.89 1.8 4.5 1.8 4.5 4.5 1.8 1.8 1.8 1.8 0.89 4.5 1.8 8.9 4.5 4.5 1.8 4.5 1.8 4.5 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0049 0.002 0.0099 0.0049 0.0049 0.002 0.0049 0.002 0.0049 0.002 0.0049 0.002 0.0049 0.00099 0.002 0.0049 0.002 0.002 0.002 0.002 0.002 0.0049 0.002 0.0018 17000 79 1.1 5.6 19 4 24 1400 170 39 39 2.3 0.28 4.4 0.059 8.1 4.2 0.18 13 0.43 0.24 0.22 0.014 0.0045 0.0045 0.00089 0.0018 0.0018 0.0045 0.0018 0.0018 0.0045 0.0018 0.0045 0.00089 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.045 0.0089 0.0045 0.0089 0.0018 0.0045 0.0045 0.0018 0.0045 0.0045 0.00089 0.0018 0.0045 0.0018 0.0045 0.0045 0.0018 0.0018 0.0018 0.0018 0.00089 0.0045 0.0018 0.0089 0.0045 0.0045 0.0018 0.0045 0.0018 0.0045 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H J A U J A J A U J F, RL changed from 140 and  MDL from 67 A J J J J A,Q J J J Q Q Q J J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Boeing Soil Char Level  (mg/kg) 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 203.8 4.8 22 60.11 26.18 64.4 7524 Exceeds Boeing Soil Char Level No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No No No No No No No No Ratio Boeing Soil Char Level 1.20E‐04 8.66E‐04 1.21E‐06 No SL 1.65E‐03 6.06E‐04 8.03E‐05 2.74E‐05 3.06E‐04 5.88E‐04 3.06E‐04 5.41E‐04 5.00E‐03 No SL 9.52E‐06 4.45E‐03 4.81E‐03 3.39E‐05 2.34E‐05 No SL 2.51E‐03 2.88E‐05 9.80E‐02 5.29E‐04 4.49E‐01 3.88E‐01 2.29E‐01 2.55E‐01 3.16E‐01 1.53E‐01 3.73E‐01 1.86E‐01 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No 2.25E‐01 3.49E‐01 2.55E‐01 2.16E‐01 5.60E‐01 1.82E‐01 1.36E‐01 1.93E‐01 1.24E‐01 1.10E‐01 2.02E‐01 4.30E‐01 2.42E‐01 2.89E‐01 1.61E‐02 4.50E‐04 2.05E‐01 3.10E‐04 7.32E‐07 6.25E‐03 2.05E‐05 3.38E‐03 9.52E‐04 6.52E‐04 No SL 4.50E‐04 No SL 5.81E‐04 4.60E‐02 1.73E‐02 1.38E‐05 6.90E‐03 4.10E‐03 5.63E‐04 7.83E‐05 No SL 1.35E‐03 No SL 4.50E+00 3.87E‐04 1.00E‐03 1.93E‐04 1.57E‐02 1.80E‐04 No SL 9.23E‐03 1.96E‐04 1.41E‐03 1.25E‐02 8.57E‐05 No SL 2.46E‐03 1.41E‐03 No SL 1.95E‐04 No SL 1.38E‐03 2.47E‐04 3.99E‐05 1.10E‐04 7.79E‐04 1.09E‐06 No SL 1.52E‐03 5.45E‐04 7.38E‐05 2.47E‐05 2.81E‐04 SCL Basis Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units RL RL Units MDL MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.9 2 9.9 4.9 4.9 2 4.9 2 4.9 2 4.9 2 4.9 0.99 2 4.9 2 2 2 2 2 4.9 2 1.8 11 0.56 0.34 5.6 1.1 0.56 7.1 110 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.36 0.8 1.9 1.2 0.87 1.3 0.59 0.5 0.6 0.74 0.78 0.53 0.51 0.44 0.66 0.56 0.79 0.71 0.43 0.46 0.59 0.47 0.31 1.2 5.5 0.27 0.17 1.1 0.45 0.11 0.34 46 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 170 1.1 5.6 28 1.1 0.56 0.23 0.23 0.45 0.11 0.45 1.1 0.23 0.23 0.034 4.5 4.5 0.89 1.8 1.8 4.5 1.8 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.5 45 8.9 4.5 8.9 1.8 4.5 4.5 1.8 4.5 4.5 0.89 1.8 4.5 1.8 4.5 4.5 1.8 1.8 1.8 1.8 0.89 4.5 1.8 8.9 4.5 4.5 1.8 4.5 1.8 4.5 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 170 0.7 1.1 0.77 0.014 0.017 0.0069 0.091 0.056 0.018 0.045 0.09 0.005 0.0034 0.0062 0.39 0.52 0.63 0.49 0.62 0.4 0.8 0.52 0.62 0.54 0.5 0.69 0.57 0.52 0.53 0.5 0.62 0.54 0.56 0.57 0.53 0.63 0.55 4.5 1.6 0.94 3.4 0.48 0.54 0.55 0.48 0.48 0.49 0.45 0.6 0.62 0.57 0.39 0.78 0.59 0.25 0.58 0.62 0.41 0.33 0.72 1.7 1.1 0.78 1.2 0.54 0.45 0.54 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y N N Y N N Y Y N Y N N N N Y N Y Y N Y N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N Y N N Y N N N N N N N N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018X060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 ELBS1018S060 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 3/26/08 11:55 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum Barium Beryllium Boron Cobalt Copper Lithium Molybdenum Potassium Silver Sodium Vanadium Zinc Zirconium Arsenic Cadmium Chromium Lead Nickel Selenium Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Page 25 of 108 CAS Number 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 7440393 7440417 7440428 7440484 7440508 7439932 7439987 7440097 7440224 7440235 7440622 7440666 7440677 7440382 7440439 7440473 7439921 7440020 7782492 7440280 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 Result  Value 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 5 15100 70.7 0.699 5.26 4.91 9.79 22.3 0.268 1720 0.182 178 35.3 38.2 3.74 4.73 0.284 20.9 5.27 13.2 1.03 0.234 0.0113 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 19 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 2 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0018 0.0045 0.0018 0.0045 0.00089 0.0018 0.0045 0.0018 0.0018 0.0018 0.0018 0.0018 0.0045 0.0018 0.005 15100 70.7 0.699 5.35 4.91 9.79 22.3 1.07 1720 0.535 178 35.3 38.2 3.74 4.73 0.284 20.9 5.27 13.2 2.21 0.234 0.106 0.005 0.005 0.005 0.005 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.01 0.019 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N Y Y Y N Y Y Y N Y N Y Y Y Y Y Y Y Y Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U Validation Note $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Q, Q B U B U Q, Q, B U J J J U J UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Q, Q B, , B Q Q Q, Q, B, , B Q, Q Q, Q B,H Q, Q Q Q, Q, L Q F Q F, B Boeing Soil Char Level  (mg/kg) 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 203.8 4.8 22 26.18 42 64.4 1.642 7524 0.99 754 111.8 153 10.64 24.2 0.435 60.11 33.9 64.2 1 0.761 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 Exceeds Boeing Soil Char Level No No No No No SL No No No No No No SL No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No Ratio Boeing Soil Char Level 5.29E‐04 2.81E‐04 4.86E‐04 4.59E‐03 No SL 8.57E‐06 4.09E‐03 4.33E‐03 3.05E‐05 2.11E‐05 No SL 2.26E‐03 2.65E‐05 8.82E‐02 1.47E‐03 3.98E‐01 3.47E‐01 1.46E‐01 2.43E‐01 1.88E‐01 2.33E‐01 3.46E‐01 6.52E‐01 2.29E‐01 5.40E‐01 2.36E‐01 3.16E‐01 2.50E‐01 3.52E‐01 1.95E‐01 6.53E‐01 3.48E‐01 1.55E‐01 2.06E‐01 2.21E+00 3.07E‐01 1.22E‐01 5.00E‐04 2.27E‐01 1.74E‐03 2.03E‐06 1.74E‐02 4.55E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 4.35E‐04 2.22E‐03 4.13E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 3.85E‐03 6.87E‐04 2.24E‐04 1.22E‐04 2.16E‐03 1.23E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 1.8 4.5 1.8 4.5 0.89 1.8 4.5 1.8 1.8 1.8 1.8 1.8 4.5 1.8 5 21.4 0.535 0.535 5.35 0.535 1.07 0.54 1.07 53.5 0.535 107 0.535 2.14 5.35 2.21 0.276 2.21 1.1 2.21 2.21 0.551 0.106 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 19 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.67 0.7 0.48 0.46 0.4 0.6 0.51 0.71 0.64 0.39 0.42 0.54 0.43 0.28 1 3.59 0.0246 0.0728 0.664 0.139 0.214 0.11 0.268 3.54 0.182 37.3 0.171 0.701 1.07 0.221 0.106 0.662 0.165 0.628 1.03 0.165 0.0113 1 2 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 3 3 7 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 1 2 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N Y Y N N Y N Y N N Y Y Y Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1018 ELBS1018 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1018X060 ELBS1018X060 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S010 ELBS1019S060 ELBS1019S060 EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1018S060 ELBS1018S060 Sample ID Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 11:55 3/26/08 11:55 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:30 3/27/08 8:45 3/27/08 8:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5.5 5.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5.5 5.5 Sample  Bottom  Depth (feet bgs) 6 6 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 Soil Soil Soil Soil Soil Soil 5.5 5.5 5.5 5.5 5.5 5.5 6 6 6 6 6 6 Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result VOCs VOCs VOCs Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals 8260B 8260B 8260B 9045C 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B Trichlorofluoromethane Vinyl chloride Xylenes, Total pH Aluminum Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum 75694 75014 1330207 E‐10139 7429905 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 7429905 In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals 6010B 6010B 6010B 6010B 6020 6020 Antimony Boron Potassium Sodium Arsenic Barium 7440360 7440428 7440097 7440235 7440382 7440393 Page 26 of 108 Result  Value 5 5 0.372 7.66 4440 0.316 1.02 2590 131 5 153 0.16 0.13 6.9 7.6 19.7 5.4 12.4 0.3 11.4 0.519 3.5 0.16 34.5 50.1 1.1 0.0075 0.964 0.964 0.964 0.964 0.964 4.82 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 4.82 4.82 0.964 4.82 0.964 4.82 4.82 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.372 4.82 0.964 0.964 0.964 0.964 0.964 0.964 0.723 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 1.36 9530 0.517 1.1 1360 169 2.8 69.1 Result  Value  Units ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.005 mg/kg 0.005 mg/kg 0.000372 mg/kg 7.66 ph Units 4440 mg/kg 1.02 mg/kg 5.1 mg/kg 2590 mg/kg 131 mg/kg 5 mg/kg 153 mg/kg 0.16 mg/kg 0.13 mg/kg 6.9 mg/kg 7.6 mg/kg 19.7 mg/kg 5.4 mg/kg 12.4 mg/kg 0.3 mg/kg 11.4 mg/kg 1.04 mg/kg 3.5 mg/kg 0.16 mg/kg 34.5 mg/kg 50.1 mg/kg 1.1 mg/kg 0.0075 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.00482 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.00482 mg/kg 0.00482 mg/kg 0.000964 mg/kg 0.00482 mg/kg 0.000964 mg/kg 0.00482 mg/kg 0.00482 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000372 mg/kg 0.00482 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000723 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.000964 mg/kg 0.00136 mg/kg 9530 mg/kg 1.1 5.51 1360 169 2.8 69.1 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N Y Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N Y N N N N N N N N Y Y U U N N Y Y Y Y UJ UJ J J J J UJ UJ J J J Validation Note *III I I *III Q E J J J J Q Q, *III E U J J Q, E J A J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U J U U U U U U U U B, B, B, B J *III I, $, MDL and result changed  from 0.342 I *III Q E Boeing Soil Char Level  (mg/kg) 170 0.0204 3.4 ‐‐ 37900 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 0.761 111.8 153 10.64 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 37900 Exceeds Boeing Soil Char Level No No No No SL No Yes No No No No No No No No No No No No No No Yes Yes No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No Ratio Boeing Soil Char Level 2.94E‐05 2.45E‐01 1.09E‐04 No SL 1.17E‐01 2.04E+00 2.32E‐01 3.44E‐01 1.74E‐01 2.07E‐01 7.51E‐01 3.33E‐02 2.99E‐01 1.15E‐01 2.90E‐01 4.69E‐01 1.59E‐01 1.93E‐01 1.83E‐01 1.78E‐01 1.04E+00 3.54E+00 2.10E‐01 3.09E‐01 3.27E‐01 1.03E‐01 8.62E‐03 9.64E‐05 4.38E‐02 3.36E‐04 3.92E‐07 3.35E‐03 2.19E‐05 1.81E‐03 5.10E‐04 1.40E‐04 No SL 9.64E‐05 No SL 3.11E‐04 9.86E‐03 9.27E‐03 7.42E‐06 3.69E‐03 2.20E‐03 3.01E‐04 4.19E‐05 No SL 7.25E‐04 No SL 5.91E‐07 4.82E‐01 6.03E‐05 2.10E‐04 6.03E‐05 1.07E‐03 1.05E‐04 8.38E‐03 3.86E‐05 No SL 4.94E‐03 4.19E‐05 3.01E‐04 1.36E‐02 4.59E‐05 No SL 1.32E‐03 3.01E‐04 1.05E‐04 No SL 1.32E‐04 4.32E‐05 2.35E‐05 4.17E‐04 7.42E‐04 1.13E‐04 1.62E‐03 No SL 1.58E‐05 1.32E‐05 2.84E‐04 2.61E‐04 9.84E‐04 3.44E‐06 8.76E‐04 2.32E‐03 1.63E‐05 1.13E‐05 No SL 1.21E‐03 5.67E‐06 4.73E‐02 4.00E‐04 2.51E‐01 0.5 22 7524 754 24.2 203.8 Yes No No No No No 2.20E+00 2.50E‐01 1.81E‐01 2.24E‐01 1.16E‐01 3.39E‐01 Samples  Samples  Best  included in  included in  Pick? ERA HHRA SCL Units RL RL Units MDL MDL  Units Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5 5 1.93 0.1 20.4 1.02 5.1 15.3 15.3 1.04 0.415 0.104 0.208 0.623 0.208 0.208 0.415 2.08 0.104 0.415 1.04 0.208 0.208 10.4 2.08 0.415 0.00981 0.964 0.964 0.964 0.964 0.964 4.82 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 4.82 4.82 0.964 4.82 0.964 4.82 4.82 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 1.93 4.82 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 0.964 1.86 22 ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 2 1 0.241 0.01 6.94 0.316 1.02 5.1 4.59 0.311 0.104 0.0208 0.0208 0.208 0.0208 0.0415 0.104 0.415 0.0208 0.104 0.519 0.0415 0.0415 2.08 0.417 0.104 0.00147 0.289 0.482 0.193 0.289 0.241 0.964 0.289 0.289 0.289 0.241 0.241 0.482 0.193 0.482 0.193 0.193 0.241 0.289 0.193 0.193 0.289 0.193 0.289 1.64 1.21 0.193 1.47 0.231 1.05 2.49 0.318 0.193 0.482 0.193 0.289 0.482 0.193 0.193 0.482 0.193 0.482 0.289 0.193 0.289 0.289 0.482 0.193 0.193 0.241 1.93 0.193 0.193 0.193 0.193 0.241 0.193 0.193 0.193 0.193 0.28 0.289 0.289 0.241 0.482 0.482 0.232 7.49 ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y MRL Ecological RBSL Background Background Background Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y SCL Basis Ecological RBSL Suburban Residential RBSL Ecological RBSL Background MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL 1.1 5.51 16.5 16.5 1.08 0.431 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.517 1.1 5.51 4.96 0.324 0.108 Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1019 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1019S060 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 3/27/08 8:45 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 1 1 1 1 1 1 1 1 1 1 EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Metals Metals Metals Metals 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 9045C 6010B 6010B 6010B 6010B Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH Aluminum Antimony Boron Potassium 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 7429905 7440360 7440428 7440097 In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6020 6020 6020 6020 6020 6020 6020 Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 Page 27 of 108 Result  Value 0.48 0.058 20 3 8.3 9.4 18.4 0.73 9.3 0.539 0.23 0.18 25.8 45.4 1.7 0.027 0.929 0.929 0.929 0.929 0.929 4.65 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 4.65 4.65 0.929 4.65 0.929 4.65 4.65 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.312 0.929 1.36 4.65 0.929 0.929 0.929 0.929 0.929 0.929 0.682 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 2.03 3.65 3.65 3.65 3.65 7.62 15500 0.331 1.3 1990 99.2 4.9 114 0.79 0.12 20.2 6.6 7.8 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.48 mg/kg 0.058 mg/kg 20 mg/kg 3 mg/kg 8.3 mg/kg 9.4 mg/kg 18.4 mg/kg 0.73 mg/kg 9.3 mg/kg 1.08 mg/kg 0.23 mg/kg 0.18 mg/kg 25.8 mg/kg 45.4 mg/kg 1.7 mg/kg 0.027 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.00465 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.00465 mg/kg 0.00465 mg/kg 0.000929 mg/kg 0.00465 mg/kg 0.000929 mg/kg 0.00465 mg/kg 0.00465 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000312 mg/kg 0.000929 mg/kg 0.00136 mg/kg 0.00465 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000682 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.000929 mg/kg 0.00203 mg/kg 3.65 mg/kg 3.65 mg/kg 3.65 mg/kg 3.65 mg/kg 7.62 ph Units 15500 mg/kg 1.07 mg/kg 1.3 mg/kg 1990 mg/kg 99.2 4.9 114 0.79 0.12 20.2 6.6 7.8 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N N N N N N N Y N N N N N N N N N N N N N Y Y N Y Y N Y Y Y Y Y Y Y Project  Qual  Code Validation Note J J J J Q Q, *III E U J J Q, E J A J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U J U U U U U U U J U U U U U U U U U U U U U B, B, B, B UJ J I U J F, RL CHANGED FROM 16 AND  MDL CHANGED FROM 4.81 Boeing Soil Char Level  (mg/kg) 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 0.761 111.8 153 10.64 0.87 10 0.022 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ 37900 0.5 22 7524 Exceeds Boeing Soil Char Level No No No No No No No No No Yes No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No No No Yes No SL No Yes No No Ratio Boeing Soil Char Level 1.00E‐01 1.33E‐01 3.33E‐01 1.15E‐01 1.98E‐01 2.77E‐01 2.86E‐01 4.45E‐01 1.45E‐01 1.08E+00 2.32E‐01 2.37E‐01 2.31E‐01 2.97E‐01 1.60E‐01 3.10E‐02 9.29E‐05 4.22E‐02 3.24E‐04 3.78E‐07 3.23E‐03 2.11E‐05 1.74E‐03 4.92E‐04 1.35E‐04 No SL 9.29E‐05 No SL 3.00E‐04 9.50E‐03 8.93E‐03 7.15E‐06 3.56E‐03 2.12E‐03 2.90E‐04 4.04E‐05 No SL 6.98E‐04 No SL 5.70E‐07 4.65E‐01 5.81E‐05 2.02E‐04 5.81E‐05 1.03E‐03 1.01E‐04 8.08E‐03 3.72E‐05 No SL 4.76E‐03 4.04E‐05 2.90E‐04 1.31E‐02 4.42E‐05 No SL 1.27E‐03 2.90E‐04 1.01E‐04 No SL 1.28E‐04 4.17E‐05 2.27E‐05 1.35E‐04 7.15E‐04 4.12E‐04 1.57E‐03 No SL 1.52E‐05 1.27E‐05 2.73E‐04 2.51E‐04 9.48E‐04 3.25E‐06 8.45E‐04 2.23E‐03 1.57E‐05 1.09E‐05 No SL 1.17E‐03 5.46E‐06 4.55E‐02 5.97E‐04 2.61E‐03 2.61E‐03 2.61E‐03 3.65E+00 No SL 4.09E‐01 2.14E+00 5.91E‐02 2.64E‐01 754 24.2 203.8 4.8 0.435 60.11 26.18 42 No No No No No No No No 1.32E‐01 2.02E‐01 5.59E‐01 1.65E‐01 2.76E‐01 3.36E‐01 2.52E‐01 1.86E‐01 SCL Basis Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL SCL Units Background MRL Ecological RBSL Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg Background Background Background Ecological RBSL Background Background Background Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL RL 0.108 0.216 0.647 0.216 0.216 0.431 2.16 0.108 0.431 1.08 0.216 0.216 10.8 2.19 0.431 0.0101 0.929 0.929 0.929 0.929 0.929 4.65 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 4.65 4.65 0.929 4.65 0.929 4.65 4.65 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 1.86 4.65 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 0.929 2.03 3.65 3.65 3.65 3.65 0.1 21.4 1.07 5.34 16 99.2 1.08 0.431 0.539 0.216 3.24 1.08 1.08 Samples  Samples  Best  included in  included in  Pick? ERA HHRA RL Units MDL MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg 0.0216 0.0216 0.216 0.0216 0.0431 0.108 0.431 0.0216 0.108 0.539 0.0431 0.0431 2.16 0.437 0.108 0.00152 0.279 0.465 0.186 0.279 0.232 0.929 0.279 0.279 0.279 0.232 0.232 0.465 0.186 0.465 0.186 0.186 0.232 0.279 0.186 0.186 0.279 0.186 0.279 1.58 1.16 0.186 1.41 0.223 1.01 2.4 0.307 0.186 0.465 0.186 0.279 0.465 0.186 0.186 0.465 0.186 0.465 0.279 0.186 0.279 0.279 0.465 0.186 0.186 0.232 1.86 0.186 0.186 0.186 0.186 0.232 0.186 0.186 0.186 0.186 0.27 0.279 0.279 0.232 0.465 0.465 0.254 1.2 1.2 1.2 1.2 0.01 7.26 0.331 1.07 5.34 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 99.2 0.324 0.108 0.108 0.0216 1.08 0.108 0.216 Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6020 6020 6020 6020 7471A 8260B 8260B Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440280 7440622 7440666 7440677 7439976 120821 87683 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1020S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Result  Value  Units Result  in SL Units SL Units Detected Project  Qual  Code In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals 6020 6020 6020 6020 6020 6020 Lead Lithium Molybdenum Nickel Selenium Silver 7439921 7439932 7439987 7440020 7782492 7440224 7.2 20.9 0.44 12.4 0.539 0.057 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 7.2 20.9 0.44 12.4 1.08 0.057 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y N Y 0.25 44.5 45.7 2.2 0.0036 1.01 1.01 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.25 44.5 45.7 2.2 0.0036 0.00101 0.00101 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y N N U 18.2 18.2 5.97 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 1.01 1.01 1.01 5.07 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 5.07 5.07 1.01 5.07 1.01 5.07 5.07 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 2.03 5.07 1.01 1.01 1.01 1.01 1.01 1.01 0.291 1.01 1.01 1.01 1.01 1.01 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0182 0.0182 0.00597 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.0182 0.00101 0.00101 0.00101 0.00507 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00507 0.00507 0.00101 0.00507 0.00101 0.00507 0.00507 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.00203 0.00507 0.00101 0.00101 0.00101 0.00101 0.00101 0.00101 0.000291 0.00101 0.00101 0.00101 0.00101 0.00101 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N U U J U U U U U U U U U U U U U U U U U U U U U U UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ J UJ UJ UJ UJ UJ Page 28 of 108 Validation Note U J J UJ UJ F, RL CHANGED FROM 0.216  AND MDL CHANGED FROM  0.0431 B, B, B, B H H B, RESULT CHANGED FROM  8.04 H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H Boeing Soil Char Level  (mg/kg) 33.9 64.4 1.642 64.2 1 0.99 Exceeds Boeing Soil Char Level No No No No Yes No Ratio Boeing Soil Char Level 2.12E‐01 3.25E‐01 2.68E‐01 1.93E‐01 1.08E+00 5.76E‐02 Background Background Background Background MRL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.761 111.8 153 10.64 0.87 10 0.022 No No No No No No No 3.29E‐01 3.98E‐01 2.99E‐01 2.07E‐01 4.14E‐03 1.01E‐04 4.59E‐02 Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL 5.69E‐02 2.02E‐04 2.60E‐03 4.04E‐03 1.65E‐01 1.40E‐03 5.60E‐01 2.50E‐03 3.43E‐04 1.65E‐02 5.52E‐02 8.27E‐03 4.70E‐02 4.70E‐01 4.70E‐02 2.46E‐03 4.70E‐02 1.52E‐02 1.61E‐01 3.37E‐04 2.04E‐02 4.70E‐02 1.25E‐03 1.40E‐02 1.52E‐02 3.52E‐04 4.11E‐07 3.51E‐03 2.30E‐05 1.89E‐03 5.34E‐04 1.46E‐04 No SL 1.01E‐04 No SL 3.26E‐04 1.03E‐02 9.71E‐03 7.77E‐06 3.87E‐03 2.30E‐03 3.16E‐04 4.39E‐05 No SL 7.59E‐04 No SL 6.21E‐07 5.07E‐01 6.31E‐05 2.20E‐04 6.31E‐05 1.13E‐03 1.10E‐04 8.78E‐03 4.04E‐05 No SL 5.18E‐03 4.39E‐05 3.16E‐04 1.42E‐02 4.81E‐05 No SL 1.38E‐03 3.16E‐04 1.10E‐04 No SL 1.39E‐04 4.53E‐05 2.46E‐05 4.37E‐04 7.77E‐04 6.15E‐04 1.71E‐03 No SL 1.66E‐05 1.38E‐05 2.97E‐04 2.73E‐04 1.03E‐03 1.39E‐06 9.18E‐04 2.43E‐03 1.71E‐05 1.18E‐05 No SL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL SCL Units RL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA RL Units MDL 0.431 10.8 0.108 2.16 1.08 0.216 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.108 2.16 0.0216 0.539 0.539 0.0431 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.25 10.8 2.16 0.431 0.00967 1.01 1.01 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.25 2.16 0.431 0.108 0.00145 0.304 0.507 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 1.01 1.01 1.01 5.07 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 5.07 5.07 1.01 5.07 1.01 5.07 5.07 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 2.03 5.07 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 1.01 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 6.01 5.47 5.47 5.47 5.47 5.47 3.64 5.47 3.64 6.09 5.47 3.64 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.72 0.203 0.304 0.254 1.01 0.304 0.304 0.304 0.254 0.254 0.507 0.203 0.507 0.203 0.203 0.254 0.304 0.203 0.203 0.304 0.203 0.304 1.73 1.27 0.203 1.54 0.244 1.11 2.62 0.335 0.203 0.507 0.203 0.304 0.507 0.203 0.203 0.507 0.203 0.507 0.304 0.203 0.304 0.304 0.507 0.203 0.203 0.254 2.03 0.203 0.203 0.203 0.203 0.254 0.203 0.203 0.203 0.203 0.294 0.304 0.304 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1020 ELBS1020 ELBS1020 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1020S010 ELBS1020S010 ELBS1020S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/1/08 13:40 4/1/08 13:40 4/1/08 13:40 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 EEL EEL EEL CC 1 EEL CC 1 Soil Boring Soil Boring ELBS1021 ELBS1021 ELBS1021S010 ELBS1021S010 Primary Sample Primary Sample 3/26/08 11:05 Soil 3/26/08 11:05 Soil 0.5 0.5 1 In Place 1 In Place Primary Result Primary Result Other SVOCs Other SVOCs 8270C SIM 8270C SIM bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate 117817 85687 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Result  Value  Units In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Metals Metals Metals Metals Metals Metals Metals Metals 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 9045C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 1.01 1.01 1.01 1.9 5.4 5.4 5.4 5.4 7.3 23000 99 1.2 1.2 23 4.5 26 1400 ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 150 42 40 2.9 0.32 16 0.11 6.7 10 0.33 16 0.32 0.12 0.22 0.033 4.9 4.9 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Page 29 of 108 Result  in SL Units Detected Project  Qual  Code Validation Note mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N Y Y Y Y Y Y Y Y Y UJ UJ UJ U U U U U H H H J A mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N 21 ug/kg 0.73 ug/kg 0.021 mg/kg 0.00073 mg/kg 21 21 1.3 4.4 21 21 21 21 21 21 0.2 0.23 0.43 0.25 0.33 21 0.45 21 21 21 21 0.36 0.97 1.9 1.9 4.9 1.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.9 49 9.7 4.9 11 1.9 4.9 4.9 1.9 4.9 4.9 0.97 1.9 4.9 1.9 4.9 4.9 1.9 1.9 1.9 0.021 0.021 0.0013 0.0044 0.021 0.021 0.021 0.021 0.021 0.021 0.0002 0.00023 0.00043 0.00025 0.00033 0.021 0.00045 0.021 0.021 0.021 0.021 0.00036 0.00097 0.0019 0.0019 0.0049 0.0019 0.0019 0.0049 0.0019 0.0049 0.00097 0.0019 0.0049 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0049 0.049 0.0097 0.0049 0.011 0.0019 0.0049 0.0049 0.0019 0.0049 0.0049 0.00097 0.0019 0.0049 0.0019 0.0049 0.0049 0.0019 0.0019 0.0019 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.00101 0.00101 0.00101 0.0019 5.4 5.4 5.4 5.4 7.3 23000 99 1.2 1.2 23 4.5 26 1400 SL Units 150 42 40 2.9 0.32 16 0.11 6.7 10 0.33 16 0.32 0.12 0.22 0.033 0.0049 0.0049 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg $ $ $ $ J J A J A U J F, RL changed from 130 and  MDL from 65 A J J J J A,Q Boeing Soil Char Level  (mg/kg) 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 Exceeds Boeing Soil Char Level No No No No No No No Yes No SL No No No No No No No No Ratio Boeing Soil Char Level 1.27E‐03 5.94E‐06 4.95E‐02 5.59E‐04 3.86E‐03 3.86E‐03 3.86E‐03 5.40E+00 No SL 6.07E‐01 4.86E‐01 2.50E‐01 5.45E‐02 3.83E‐01 1.72E‐01 4.04E‐01 1.86E‐01 Background Background Ecological RBSL Ecological RBSL Background Background Background Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 No No No No No No No No No No No No No No No No No 1.99E‐01 3.76E‐01 2.61E‐01 2.73E‐01 6.40E‐01 6.61E‐01 2.53E‐01 1.60E‐01 2.95E‐01 2.01E‐01 2.49E‐01 3.20E‐01 1.21E‐01 2.89E‐01 3.79E‐02 4.90E‐04 2.23E‐01 Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 6.56E‐02 Ecological RBSL 8.11E‐06 Ecological RBSL mg/kg mg/kg 9.13E‐03 4.67E‐03 1.18E‐02 3.38E‐04 6.46E‐01 2.88E‐03 3.96E‐04 1.91E‐02 6.36E‐02 9.55E‐03 5.17E‐04 5.94E‐03 1.11E‐03 3.38E‐05 2.75E‐04 1.86E‐01 8.33E‐06 2.36E‐02 5.43E‐02 1.44E‐03 1.62E‐02 3.00E‐04 3.38E‐04 7.72E‐07 6.60E‐03 2.23E‐05 3.56E‐03 1.01E‐03 7.10E‐04 No SL 4.90E‐04 No SL 6.13E‐04 5.01E‐02 1.83E‐02 1.46E‐05 7.28E‐03 4.33E‐03 5.94E‐04 8.26E‐05 No SL 1.43E‐03 No SL 4.90E+00 4.22E‐04 1.09E‐03 2.39E‐04 1.65E‐02 1.96E‐04 No SL 9.74E‐03 2.13E‐04 1.53E‐03 1.37E‐02 9.05E‐05 No SL 2.59E‐03 1.53E‐03 No SL 2.06E‐04 No SL 1.46E‐03 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg J J J J Q Q Q UJ UJ $,H $,H N Y U J B,$, result changed from 7.3 0.32 90 No No N N Y Y N N N N N N Y Y Y Y Y N Y N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U J J U U U U U U J J J J J U J U U U U J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ B,$, result changed from 0.59 $ 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No $ $ $ $ $ $ *III $ $ $ $ $ $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H B,$,H, RL changed from 9.7 $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H SCL Basis Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units RL RL Units 1.01 1.01 1.01 1.9 5.4 5.4 5.4 5.4 0.1 11 0.55 0.33 5.5 1.1 0.55 6.9 110 150 1.1 5.5 28 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 4.9 4.9 ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 21 ug/kg 21 ug/kg 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 0.97 1.9 1.9 4.9 1.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.9 49 9.7 4.9 11 1.9 4.9 4.9 1.9 4.9 4.9 0.97 1.9 4.9 1.9 4.9 4.9 1.9 1.9 1.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL MDL  Units 0.254 0.507 0.507 1.3 1.1 1.1 1.1 1.1 ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg 5.4 0.26 0.17 1.1 0.44 0.11 0.33 45 150 0.68 1.1 0.75 0.014 0.016 0.0068 0.089 0.055 0.018 0.044 0.088 0.0049 0.0033 0.0061 0.43 0.56 Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 3.5 ug/kg 0.18 ug/kg Y Y Y Y Y Y 0.31 0.49 0.91 0.34 0.49 0.28 0.33 0.17 0.18 0.14 0.15 0.15 0.15 0.21 0.2 0.26 0.22 0.24 0.26 0.35 0.33 0.19 0.69 0.53 0.67 0.44 0.87 0.56 0.67 0.58 0.54 0.75 0.62 0.56 0.57 0.54 0.68 0.58 0.61 0.62 0.57 0.69 0.6 4.9 1.7 1 3.7 0.52 0.59 0.6 0.52 0.52 0.53 0.49 0.65 0.68 0.62 0.43 0.84 0.64 0.27 0.63 Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1021 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1021S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/26/08 11:05 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 300.0 300.0 Analyte Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide Chloride CAS Number 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 16887006 Result  Value 1.9 0.97 4.9 1.9 9.7 4.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 4.9 1.9 1.84 3.42 1.59 2.68 3.42 0.663 7.07 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.0019 0.00097 0.0049 0.0019 0.0097 0.0049 0.0049 0.0019 0.0049 0.0019 0.0049 0.0019 0.0049 0.0019 0.0049 0.00097 0.0019 0.0049 0.0019 0.0019 0.0019 0.0019 0.0019 0.0049 0.0019 0.00184 3.42 1.59 2.68 3.42 2.01 7.07 1.83 1.01 1.01 2.01 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N N Y Project  Qual  Code UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U U J J U U EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 Soil Soil Soil Soil 0 0 0 0 1 1 1 1 In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Inorganics 300.0 300.0 300.0 300.0 Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) 16984488 NO3N NO2 14265442 1.83 0.302 0.302 1.86 EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024S010 ELBS1024S010 ELBS1024S010 Primary Sample Primary Sample Primary Sample 3/27/08 9:45 Soil 3/27/08 9:45 Soil 3/27/08 9:45 Soil 0 0 0 1 In Place 1 In Place 1 In Place Primary Result Primary Result Primary Result Inorganics Inorganics Metals 300.0 9045C 6010B Sulfate pH Aluminum 14808798 E‐10139 7429905 6.34 mg/kg 7.73 pH Units 15800 mg/kg EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 0.392 1.5 922 135 6.3 119 0.91 0.07 29.9 4.6 10 6.8 29.9 0.38 14.6 0.503 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.01 1.5 922 135 6.3 119 0.91 0.07 29.9 4.6 10 6.8 29.9 0.38 14.6 1.01 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6020 6020 6020 6020 6020 7471A 8260B 8260B Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 0.201 0.23 55.4 38.3 3.2 0.011 0.918 0.918 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.201 0.23 55.4 38.3 3.2 0.011 0.000918 0.000918 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y N N EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 0.918 0.918 0.918 4.59 0.918 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.0171 0.000918 0.000918 0.000918 0.00459 0.000918 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Page 30 of 108 mg/kg mg/kg mg/kg mg/kg Result  in SL Units N N N N U U U U 6.34 mg/kg N 7.73 ph Units Y 15800 mg/kg Y U J UJ J J J J Validation Note $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $ F, RL CHANGED FROM 1.01  AND MDL CHANGED FROM  0.302 $ $ B F, RL CHANGED FROM 4.02  AND MLD CHANGED FROM  1.01 *III I, $, MDL and result changed  from 0.314 I *III Q E J J J J Q Q, *III E U UJ F, RESULT CHANGED FROM  0.094 AND MDL CHANGED  FROM 0.0402, Q, E J A J U U B, B, B, B B, RESULT CHANGED FROM  7.54 Boeing Soil Char Level  (mg/kg) 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No No No Yes No SL No SL 35 2340 ‐‐ 863.2 No No No SL No ‐‐ ‐‐ 37900 No SL No SL No 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 Ratio Boeing Soil Char Level 2.61E‐04 4.35E‐05 1.20E‐04 8.23E‐04 1.19E‐06 No SL 1.65E‐03 5.76E‐04 8.03E‐05 2.60E‐05 3.06E‐04 5.59E‐04 3.06E‐04 5.14E‐04 5.00E‐03 No SL 9.05E‐06 4.45E‐03 4.57E‐03 3.22E‐05 2.23E‐05 No SL 2.38E‐03 2.88E‐05 9.31E‐02 5.41E‐04 2.44E‐03 1.14E‐03 1.91E‐03 3.42E+00 No SL No SL SCL Basis Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.9 0.97 4.9 1.9 9.7 4.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 1.9 4.9 0.97 1.9 4.9 1.9 1.9 1.9 1.9 1.9 4.9 1.9 1.84 3.42 3.42 3.42 3.42 2.01 2.01 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.68 0.45 0.36 0.79 1.9 1.2 0.85 1.3 0.58 0.5 0.59 0.73 0.77 0.52 0.5 0.44 0.65 0.55 0.78 0.7 0.43 0.46 0.58 0.47 0.3 0.229 1.13 1.13 1.13 1.13 0.663 0.663 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 5.23E‐02 Ecological RBSL 4.32E‐04 Ecological RBSL No SL 2.33E‐03 Background mg/kg mg/kg mg/kg mg/kg 1.83 1.01 1.01 2.01 mg/kg mg/kg mg/kg mg/kg 1.83 0.302 0.302 0.663 mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y No SL No SL 4.17E‐01 Background mg/kg ph Units mg/kg 6.34 mg/kg 0.1 pH Units 20.2 mg/kg 6.34 mg/kg Y 0.01 pH Units Y 6.88 mg/kg Y Y Y Y Y Y Y Yes No No No No No No No No No No No No No No Yes 2.02E+00 6.82E‐02 1.23E‐01 1.79E‐01 2.60E‐01 5.84E‐01 1.90E‐01 1.61E‐01 4.97E‐01 1.76E‐01 2.38E‐01 2.01E‐01 4.64E‐01 2.31E‐01 2.27E‐01 1.01E+00 MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.01 5.06 15.2 15.2 1.01 0.402 0.101 0.201 3.02 1.01 1.01 0.402 10.1 0.101 2.01 1.01 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.392 1.01 5.06 4.55 0.302 0.101 0.0201 0.0201 1.01 0.101 0.201 0.101 2.01 0.0201 0.503 0.503 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.99 0.761 111.8 153 10.64 0.87 10 0.022 No No No No No No No No 2.03E‐01 3.02E‐01 4.96E‐01 2.50E‐01 3.01E‐01 1.26E‐02 9.18E‐05 4.17E‐02 Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.201 0.201 10.1 1.97 0.402 0.00894 0.918 0.918 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.201 0.0402 2.01 0.393 0.101 0.00134 0.275 0.459 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No 5.34E‐02 1.90E‐04 7.43E‐03 3.80E‐03 1.55E‐01 1.32E‐03 5.26E‐01 2.35E‐03 3.23E‐04 1.55E‐02 5.18E‐02 7.77E‐03 4.42E‐02 4.42E‐01 4.42E‐02 2.31E‐03 4.42E‐02 1.43E‐02 1.51E‐01 3.17E‐04 1.92E‐02 4.42E‐02 1.17E‐03 1.32E‐02 1.43E‐02 3.20E‐04 3.73E‐07 3.19E‐03 2.09E‐05 1.72E‐03 Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 17.1 0.918 0.918 0.918 4.59 0.918 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.65 5.14 5.14 5.14 5.14 5.14 3.42 5.14 3.42 5.72 5.14 3.42 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.38 0.184 0.275 0.229 0.918 0.275 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S010 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 9:45 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 300.0 300.0 Analyte 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide Chloride CAS Number 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 16887006 Result  Value 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 4.59 4.59 0.918 4.59 0.918 4.59 4.59 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 1.84 4.59 0.918 0.918 0.918 0.918 0.918 0.918 0.562 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 1.86 3.63 2.54 12.3 3.63 0.705 2.02 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.00459 mg/kg 0.00459 mg/kg 0.000918 mg/kg 0.00459 mg/kg 0.000918 mg/kg 0.00459 mg/kg 0.00459 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.00184 mg/kg 0.00459 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000562 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.000918 mg/kg 0.00186 mg/kg 3.63 mg/kg 2.54 mg/kg 12.3 mg/kg 3.63 mg/kg 2.14 mg/kg 2.02 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N Y Y N N Y Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U J U U J EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 Soil Soil Soil Soil 5 5 5 5 6 6 6 6 In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Inorganics 300.0 300.0 300.0 300.0 Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) 16984488 NO3N NO2 14265442 1.73 0.32 0.32 0.705 mg/kg mg/kg mg/kg mg/kg 1.73 1.07 1.07 2.14 mg/kg mg/kg mg/kg mg/kg N N N N U U U U EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs 300.0 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8270C SIM 8270C SIM Sulfate Aluminum Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate 14808798 7429905 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 117817 85687 4.27 8650 0.328 1.06 1550 114 8.6 70.2 0.48 0.15 21.7 6.4 9.6 5.4 23 0.3 16.4 0.532 0.0425 0.21 32.3 48.8 1.9 0.0048 0.928 0.928 19.8 18.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg 4.27 8650 1.06 5.28 1550 114 8.6 70.2 0.48 0.15 21.7 6.4 9.6 5.4 23 0.3 16.4 1.06 0.213 0.21 32.3 48.8 1.9 0.0048 0.000928 0.000928 0.0198 0.0182 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y Y Y Y N N N N U J UJ UJ J J J Page 31 of 108 Validation Note $ F, RL CHANGED FROM 1.07  AND MLD CHANGED FROM  0.32 $ $ $ F, RESULT CHANGED FROM  3.26 AND MDL CHANGED  FROM 1.07 *III I I *III Q E J J J J Q Q, *III E U UJ Q, E J A J U U U U B, B, B, B B, RL CHANGED FROM 18.2 Boeing Soil Char Level  (mg/kg) 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No No No Yes No SL No SL 35 2340 ‐‐ 863.2 No No No SL No ‐‐ 37900 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 0.761 111.8 153 10.64 0.87 10 0.022 0.32 90 No SL No Yes No No No No No No No No No No No No No No Yes No No No No No No No No No No Ratio Boeing Soil Char Level 4.86E‐04 1.33E‐04 No SL 9.18E‐05 No SL 2.96E‐04 9.39E‐03 8.83E‐03 7.06E‐06 3.52E‐03 2.09E‐03 2.87E‐04 3.99E‐05 No SL 6.90E‐04 No SL 5.63E‐07 4.59E‐01 5.74E‐05 2.00E‐04 5.74E‐05 1.02E‐03 9.98E‐05 7.98E‐03 3.67E‐05 No SL 4.71E‐03 3.99E‐05 2.87E‐04 1.29E‐02 4.37E‐05 No SL 1.25E‐03 2.87E‐04 9.96E‐05 No SL 1.26E‐04 4.12E‐05 2.24E‐05 3.97E‐04 7.06E‐04 5.58E‐04 1.55E‐03 No SL 1.50E‐05 1.26E‐05 2.70E‐04 2.48E‐04 9.37E‐04 2.68E‐06 8.35E‐04 2.21E‐03 1.56E‐05 1.08E‐05 No SL 1.15E‐03 5.40E‐06 4.50E‐02 5.47E‐04 2.59E‐03 1.81E‐03 8.79E‐03 3.63E+00 No SL No SL SCL Basis Suburban Residential RBSL Ecological RBSL SCL Units RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 4.59 4.59 0.918 4.59 0.918 4.59 4.59 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 1.84 4.59 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 0.918 1.86 3.63 3.63 3.63 3.63 2.14 2.14 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.275 0.275 0.229 0.229 0.459 0.184 0.459 0.184 0.184 0.229 0.275 0.184 0.184 0.275 0.184 0.275 1.56 1.15 0.184 1.39 0.22 1 2.37 0.303 0.184 0.459 0.184 0.275 0.459 0.184 0.184 0.459 0.184 0.459 0.275 0.184 0.275 0.275 0.459 0.184 0.184 0.229 1.84 0.184 0.184 0.184 0.184 0.229 0.184 0.184 0.184 0.184 0.266 0.275 0.275 0.229 0.459 0.459 0.232 1.2 1.2 1.2 1.2 0.705 0.705 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 4.94E‐02 Ecological RBSL 4.57E‐04 Ecological RBSL No SL 2.48E‐03 Background mg/kg mg/kg mg/kg mg/kg 1.73 1.07 1.07 2.14 mg/kg mg/kg mg/kg mg/kg 1.73 0.32 0.32 0.705 mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y No SL 2.28E‐01 2.12E+00 2.40E‐01 2.06E‐01 1.51E‐01 3.55E‐01 3.44E‐01 1.00E‐01 3.45E‐01 3.61E‐01 2.44E‐01 2.29E‐01 1.59E‐01 3.57E‐01 1.83E‐01 2.55E‐01 1.06E+00 2.15E‐01 2.76E‐01 2.89E‐01 3.19E‐01 1.79E‐01 5.52E‐03 9.28E‐05 4.22E‐02 6.19E‐02 2.02E‐04 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.27 21.1 1.06 5.28 15.9 15.9 1.06 0.425 0.106 0.213 0.638 0.213 0.213 0.425 10.6 0.106 0.425 1.06 0.213 0.213 10.6 2.09 0.425 0.00952 0.928 0.928 19.8 18.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg 4.27 7.19 0.328 1.06 5.28 4.76 0.319 0.106 0.0213 0.0213 0.213 0.0213 0.0425 0.106 2.13 0.0213 0.106 0.532 0.0425 0.0425 2.13 0.417 0.106 0.00143 0.278 0.464 6.01 5.46 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1024 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1024S060 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:00 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 1 1 1 1 1 1 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9045C Analyte Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide Chloride Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate pH Page 32 of 108 CAS Number 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 16887006 16984488 NO3N NO2 14265442 14808798 E‐10139 Result  Value 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 0.928 0.928 0.928 4.64 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 4.64 4.64 0.928 4.64 0.928 4.64 4.64 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 1.86 4.64 0.928 0.928 0.928 0.928 0.928 0.928 0.374 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 1.9 3.48 3.48 1.54 3.48 0.671 1.97 3.15 0.305 0.305 0.671 1.02 7.34 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units Result  in SL Units SL Units 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.0182 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.00464 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.00464 mg/kg 0.00464 mg/kg 0.000928 mg/kg 0.00464 mg/kg 0.000928 mg/kg 0.00464 mg/kg 0.00464 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.00186 mg/kg 0.00464 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000374 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.000928 mg/kg 0.0019 mg/kg 3.48 mg/kg 3.48 mg/kg 1.54 mg/kg 3.48 mg/kg 2.03 mg/kg 1.97 mg/kg 3.15 1.02 1.02 2.03 4.07 7.34 mg/kg mg/kg mg/kg mg/kg mg/kg ph Units Detected Project  Qual  Code N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N Y N N Y U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U J U U J N N N N N Y U U U U U Validation Note $ F, RL CHANGED FROM 1.02  AND MDL CHANGED FROM  0.305 $ $ $ $ Boeing Soil Char Level  (mg/kg) 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No No No Yes No SL No SL 35 2340 ‐‐ 863.2 ‐‐ ‐‐ No No No SL No No SL No SL Ratio Boeing Soil Char Level 7.91E‐03 4.04E‐03 1.65E‐01 1.40E‐03 5.60E‐01 2.50E‐03 3.43E‐04 1.65E‐02 5.52E‐02 8.27E‐03 4.70E‐02 4.70E‐01 4.70E‐02 2.46E‐03 4.70E‐02 1.52E‐02 1.61E‐01 3.37E‐04 2.04E‐02 4.70E‐02 1.25E‐03 1.40E‐02 1.52E‐02 3.23E‐04 3.77E‐07 3.22E‐03 2.11E‐05 1.74E‐03 4.91E‐04 1.34E‐04 No SL 9.28E‐05 No SL 2.99E‐04 9.49E‐03 8.92E‐03 7.14E‐06 3.56E‐03 2.11E‐03 2.90E‐04 4.03E‐05 No SL 6.98E‐04 No SL 5.69E‐07 4.64E‐01 5.80E‐05 2.02E‐04 5.80E‐05 1.03E‐03 1.01E‐04 8.07E‐03 3.71E‐05 No SL 4.76E‐03 4.03E‐05 2.90E‐04 1.31E‐02 4.42E‐05 No SL 1.27E‐03 2.90E‐04 1.01E‐04 No SL 1.27E‐04 4.16E‐05 2.26E‐05 4.02E‐04 7.14E‐04 5.64E‐04 1.56E‐03 No SL 1.52E‐05 1.27E‐05 2.73E‐04 2.51E‐04 9.47E‐04 1.78E‐06 8.44E‐04 2.23E‐03 1.57E‐05 1.09E‐05 No SL 1.16E‐03 5.46E‐06 4.55E‐02 5.59E‐04 2.49E‐03 2.49E‐03 1.10E‐03 3.48E+00 No SL No SL SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL 9.00E‐02 Ecological RBSL 4.36E‐04 Ecological RBSL No SL 2.35E‐03 Background No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units RL RL Units 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 18.2 0.928 0.928 0.928 4.64 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 4.64 4.64 0.928 4.64 0.928 4.64 4.64 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 1.86 4.64 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 0.928 1.9 3.48 3.48 3.48 3.48 2.03 2.03 3.15 1.02 1.02 2.03 4.07 0.1 MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.46 5.46 5.46 5.46 3.64 5.46 3.64 6.08 5.46 3.64 5.46 5.46 5.46 5.46 5.46 5.46 5.46 5.46 5.46 5.46 5.46 5.46 5.72 0.186 0.278 0.232 0.928 0.278 0.278 0.278 0.232 0.232 0.464 0.186 0.464 0.186 0.186 0.232 0.278 0.186 0.186 0.278 0.186 0.278 1.58 1.16 0.186 1.41 0.223 1.01 2.39 0.306 0.186 0.464 0.186 0.278 0.464 0.186 0.186 0.464 0.186 0.464 0.278 0.186 0.278 0.278 0.464 0.186 0.186 0.232 1.86 0.186 0.186 0.186 0.186 0.232 0.186 0.186 0.186 0.186 0.269 0.278 0.278 0.232 0.464 0.464 0.238 1.15 1.15 1.15 1.15 0.671 0.671 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg pH Units 3.15 0.305 0.305 0.671 1.02 0.01 mg/kg mg/kg mg/kg mg/kg mg/kg pH Units Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EEL EEL CC 1 Soil Boring ELBS1026 ELBS1026S010 Primary Sample 3/27/08 10:45 Soil Sample  Bottom  Remediation  Result Type Depth Status (feet bgs) 0 1 In Place Primary Result Metals 6010B Aluminum 7429905 14000 mg/kg 14000 mg/kg Y J EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 0.452 1.04 1470 148 3.7 104 0.81 0.091 22.7 6.1 7.1 6 22.4 0.38 13 0.504 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.04 5.2 1470 148 3.7 104 0.81 0.091 22.7 6.1 7.1 6 22.4 0.38 13 1.01 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y Y Y Y Y Y Y Y Y Y Y Y Y N UJ UJ J J J EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6020 6020 6020 6020 6020 7471A 8260B 8260B Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 0.201 0.22 41.9 39.8 2.9 0.0052 0.952 0.952 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.201 0.22 41.9 39.8 2.9 0.0052 0.000952 0.000952 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y N N EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 0.952 0.952 0.952 4.76 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 4.76 4.76 0.952 4.76 0.952 4.76 4.76 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 1.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.0174 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.00476 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.00476 mg/kg 0.00476 mg/kg 0.000952 mg/kg 0.00476 mg/kg 0.000952 mg/kg 0.00476 mg/kg 0.00476 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.000952 mg/kg 0.0019 mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Analytical Class Analysis  Method Analyte Page 33 of 108 CAS Number Result  Value Result  Value  Units Result  in SL Units SL Units Detected Project  Qual  Code Validation Note *III I, $, MDL and result changed  from 0.322 I *III Q E J J J J Q Q, *III E U UJ F, RESULT CHANGED FROM  0.058 AND MDL CHANGED  FROM 0.0403, Q, E J A J U U B, B, B, B B, RESULT CHANGED FROM  9.52 Boeing Soil Char Level  (mg/kg) 37900 Ratio Exceeds Boeing Boeing SCL Basis Soil Char Soil Char Level Level No 3.69E‐01 Background SCL Units RL Units MDL  Units Y Y Y 2.08E+00 2.36E‐01 1.95E‐01 1.96E‐01 1.53E‐01 5.10E‐01 1.69E‐01 2.09E‐01 3.78E‐01 2.33E‐01 1.69E‐01 1.77E‐01 3.48E‐01 2.31E‐01 2.02E‐01 1.01E+00 MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.04 5.2 15.6 15.6 1.01 0.403 0.101 0.201 3.02 1.01 1.01 0.403 10.1 0.101 2.01 1.01 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.452 1.04 5.2 4.68 0.302 0.101 0.0201 0.0201 1.01 0.101 0.201 0.101 2.01 0.0201 0.504 0.504 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.99 0.761 111.8 153 10.64 0.87 10 0.022 No No No No No No No No 2.03E‐01 2.89E‐01 3.75E‐01 2.60E‐01 2.73E‐01 5.98E‐03 9.52E‐05 4.33E‐02 Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.201 0.201 10.1 2.05 0.403 0.00965 0.952 0.952 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.201 0.0403 2.01 0.409 0.101 0.00145 0.286 0.476 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No 5.44E‐02 1.93E‐04 7.57E‐03 3.87E‐03 1.58E‐01 1.34E‐03 5.35E‐01 2.39E‐03 3.28E‐04 1.58E‐02 5.27E‐02 7.91E‐03 4.50E‐02 4.50E‐01 4.50E‐02 2.35E‐03 4.50E‐02 1.45E‐02 1.54E‐01 3.22E‐04 1.96E‐02 4.50E‐02 1.19E‐03 1.34E‐02 1.45E‐02 3.32E‐04 3.87E‐07 3.31E‐03 2.16E‐05 1.79E‐03 5.04E‐04 1.38E‐04 No SL 9.52E‐05 No SL 3.07E‐04 9.73E‐03 9.15E‐03 7.32E‐06 3.65E‐03 2.17E‐03 2.98E‐04 4.14E‐05 No SL 7.16E‐04 No SL 5.83E‐07 4.76E‐01 5.95E‐05 2.07E‐04 5.95E‐05 1.06E‐03 1.03E‐04 8.28E‐03 3.81E‐05 No SL 4.88E‐03 4.14E‐05 2.98E‐04 1.34E‐02 4.53E‐05 No SL 1.30E‐03 2.98E‐04 1.03E‐04 No SL 1.31E‐04 4.27E‐05 2.32E‐05 4.12E‐04 7.32E‐04 5.76E‐04 Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 17.4 0.952 0.952 0.952 4.76 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 4.76 4.76 0.952 4.76 0.952 4.76 4.76 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 1.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.74 5.22 5.22 5.22 5.22 5.22 3.48 5.22 3.48 5.81 5.22 3.48 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.47 0.19 0.286 0.238 0.952 0.286 0.286 0.286 0.238 0.238 0.476 0.19 0.476 0.19 0.19 0.238 0.286 0.19 0.19 0.286 0.19 0.286 1.62 1.19 0.19 1.45 0.229 1.04 2.46 0.314 0.19 0.476 0.19 0.286 0.476 0.19 0.19 0.476 0.19 0.476 0.286 0.19 0.286 0.286 0.476 0.19 0.19 0.238 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Suburban Residential RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL 7.07 mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Yes No No No No No No No No No No No No No No Yes Ecological RBSL 20.8 mg/kg MDL 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL mg/kg RL Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S010 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:45 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 300.0 300.0 Analyte Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide Chloride CAS Number 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 16887006 Result  Value 4.76 0.952 0.952 0.952 0.952 0.952 0.952 0.393 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 2.03 3.64 1.99 3.09 3.64 0.71 5.07 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 0.00476 0.000952 0.000952 0.000952 0.000952 0.000952 0.000952 0.000393 0.000952 0.000952 0.000952 0.000952 0.000952 0.000952 0.000952 0.000952 0.00203 3.64 1.99 3.09 3.64 2.15 5.07 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N Y N N N N N N N N N N Y Y N N Y Project  Qual  Code Validation Note U U U U U U U J U U U U U U U U U U J J U U $ EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Inorganics Inorganics Metals 300.0 300.0 300.0 300.0 300.0 6010B Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum 16984488 NO3N NO2 14265442 14808798 7429905 4.5 1.31 0.323 0.71 17.6 11200 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.5 1.31 1.08 2.15 17.6 11200 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y N N Y Y U F, RL CHANGED FROM 1.08  AND MLD CHANGED FROM  0.323 U U $ $ J EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B Antimony Boron Potassium Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Zirconium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440360 7440428 7440097 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7440677 7439976 120821 87683 0.376 1.07 1410 318 6.2 92 0.67 0.081 18.3 11.1 9.9 7.8 21.1 0.17 11.9 0.541 0.0433 0.2 40.9 38.4 2.1 0.0035 1.02 1.02 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 1.07 5.37 1410 318 6.2 92 0.67 0.081 18.3 11.1 9.9 7.8 21.1 0.17 11.9 1.08 0.217 0.2 40.9 38.4 2.1 0.0035 0.00102 0.00102 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y Y Y Y N N UJ UJ J J J *III I, $, MDL and result changed  from 0.333 I *III Q E EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 1.02 1.02 1.02 5.08 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.0183 0.00102 0.00102 0.00102 0.00508 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 0.00102 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Page 34 of 108 J J J J Q Q, *III E U UJ J Q, E J A J U U B, B, B, B U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U B, RESULT CHANGED FROM  15.5 Boeing Soil Char Level  (mg/kg) 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No SL No No No No No No No No No No No SL No No No No No No No Yes No SL No SL Ratio Boeing Soil Char Level 1.60E‐03 No SL 1.56E‐05 1.30E‐05 2.80E‐04 2.57E‐04 9.71E‐04 1.87E‐06 8.65E‐04 2.29E‐03 1.61E‐05 1.12E‐05 No SL 1.19E‐03 5.60E‐06 4.67E‐02 5.97E‐04 2.60E‐03 1.42E‐03 2.21E‐03 3.64E+00 No SL No SL 35 2340 ‐‐ 863.2 ‐‐ 37900 No No No SL No No SL No 1.29E‐01 5.60E‐04 No SL 2.49E‐03 No SL 2.96E‐01 0.5 22 7524 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 0.99 0.761 111.8 153 10.64 0.87 10 0.022 Yes No No No No No No No No No No No No No No Yes No No No No No No No No 2.14E+00 2.44E‐01 1.87E‐01 4.22E‐01 2.56E‐01 4.51E‐01 1.40E‐01 1.86E‐01 3.04E‐01 4.24E‐01 2.36E‐01 2.30E‐01 3.28E‐01 1.04E‐01 1.85E‐01 1.08E+00 2.19E‐01 2.63E‐01 3.66E‐01 2.51E‐01 1.97E‐01 4.02E‐03 1.02E‐04 4.64E‐02 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL 5.72E‐02 2.03E‐04 7.96E‐03 4.07E‐03 1.66E‐01 1.41E‐03 5.63E‐01 2.51E‐03 3.45E‐04 1.66E‐02 5.55E‐02 8.32E‐03 4.73E‐02 4.73E‐01 4.73E‐02 2.47E‐03 4.73E‐02 1.53E‐02 1.62E‐01 3.39E‐04 2.06E‐02 4.73E‐02 1.25E‐03 1.41E‐02 1.53E‐02 3.55E‐04 4.15E‐07 3.54E‐03 2.31E‐05 1.91E‐03 5.40E‐04 1.48E‐04 No SL 1.02E‐04 No SL 3.29E‐04 1.04E‐02 9.81E‐03 7.85E‐06 3.91E‐03 2.32E‐03 3.19E‐04 4.43E‐05 No SL SCL Basis Suburban Residential RBSL SCL Units RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.76 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 0.952 2.03 3.64 3.64 3.64 3.64 2.15 2.15 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.9 0.19 0.19 0.19 0.19 0.238 0.19 0.19 0.19 0.19 0.276 0.286 0.286 0.238 0.476 0.476 0.254 1.2 1.2 1.2 1.2 0.71 0.71 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.5 1.08 1.08 2.15 4.3 21.5 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.5 0.323 0.323 0.71 1.08 7.3 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y MRL Ecological RBSL Background Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.07 5.37 16.1 16.1 1.08 0.433 0.108 0.217 0.65 0.217 0.217 0.433 2.17 0.108 0.433 1.08 0.217 0.217 10.8 2.11 0.433 0.0102 1.02 1.02 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.376 1.07 5.37 4.83 0.325 0.108 0.0217 0.0217 0.217 0.0217 0.0433 0.108 0.433 0.0217 0.108 0.541 0.0433 0.0433 2.17 0.421 0.108 0.00153 0.305 0.508 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 18.3 1.02 1.02 1.02 5.08 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 6.04 5.49 5.49 5.49 5.49 5.49 3.66 5.49 3.66 6.11 5.49 3.66 5.49 5.49 5.49 5.49 5.49 5.49 5.49 5.49 5.49 5.49 5.49 5.49 5.74 0.203 0.305 0.254 1.02 0.305 0.305 0.305 0.254 0.254 0.508 0.203 0.508 0.203 0.203 0.254 0.305 0.203 0.203 0.305 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1026 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1026S060 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/27/08 10:50 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 EEL EEL CC 1 Soil Boring ELBS1027 ELBS1027S010 Primary Sample 3/26/08 13:45 Soil 0 EEL EEL EEL CC 1 EEL CC 1 Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027S010 ELBS1027S010 Primary Sample Primary Sample 3/26/08 13:45 Soil 3/26/08 13:45 Soil EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 1 1 1 1 1 1 1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg Result  in SL Units Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 9045C 9056 1,4‐Dichlorobenzene sec‐Dichloropropane Methyl ethyl ketone 2‐Chloroethylvinyl ether o‐Chlorotoluene 2‐Hexanone p‐Chlorotoluene Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Cumene m‐Xylene & p‐Xylene Methylene chloride Methyl tert‐butyl ether n‐Butylbenzene n‐Propylbenzene o‐Xylene p‐Cymene sec‐Butylbenzene Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) pH Bromide 106467 594207 78933 110758 95498 591786 106434 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 74953 75718 100414 98828 179601231 75092 1634044 104518 103651 95476 99876 135988 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 E‐10139 24959679 1 In Place Primary Result Inorganics 9056 Chloride 16887006 5.5 mg/kg 0 0 1 In Place 1 In Place Primary Result Primary Result Inorganics Inorganics 9056 9056 Fluoride Nitrate‐N 16984488 NO3N 5.5 mg/kg 0.87 mg/kg Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 5.5 0.56 4.8 25000 120 1.3 1.7 26 5.4 28 2000 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.5 5.5 4.8 25000 120 1.3 1.7 26 5.4 28 2000 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B 8270C SIM 8270C SIM Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 117817 85687 130 47 47 3.6 0.27 4.9 0.082 6.6 6.4 0.37 14 0.37 0.11 0.24 0.0061 4.8 4.8 22 2.7 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 22 22 2.3 22 22 22 22 0.51 0.8 3.9 9.1 6.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Page 35 of 108 1.02 1.02 5.08 5.08 1.02 5.08 1.02 5.08 5.08 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 2.03 5.08 1.02 1.02 1.02 1.02 1.02 1.02 0.528 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 4.8 5.5 5.5 12 5.5 7.5 0.43 Result  Value  Units SL Units 0.00102 mg/kg 0.00102 mg/kg 0.00508 mg/kg 0.00508 mg/kg 0.00102 mg/kg 0.00508 mg/kg 0.00102 mg/kg 0.00508 mg/kg 0.00508 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00203 mg/kg 0.00508 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.000528 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.00102 mg/kg 0.0048 mg/kg 5.5 mg/kg 5.5 mg/kg 12 mg/kg 5.5 mg/kg 7.5 ph Units 5.5 mg/kg Detected Project  Qual  Code Validation Note N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N Y N Y N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U $ $ U $ 5.5 mg/kg N U 5.5 mg/kg 0.87 mg/kg N Y U J mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y Y Y Y Y Y Y Y Y U UJ J 130 47 47 3.6 0.27 4.9 0.082 6.6 6.4 0.37 14 0.37 0.11 0.24 0.033 0.0048 0.0048 0.022 0.0027 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y U UJ UJ U J 0.022 0.022 0.0023 0.022 0.022 0.022 0.022 0.00051 0.0008 0.0039 0.0091 0.0062 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y N N N N Y Y Y Y Y U U J U U U U J J J J J U J B, result changed from 4.8 and  MDL from 2.2 F, result changed from 2.5 and  MDL from 0.91 H F, result changed from 0.51  and MDL from 0.37 H A J J A J A U J F, result changed from 88 and  MDL from 65 A J J J J J J J J A,Q Q Q Q Q,$,H Q,$,H B,$, result changed from 18 B,$, result changed from 0.75 $ $ $ $ $ Boeing Soil Char Level  (mg/kg) 1.33 ‐‐ 8160 0.01 16 23 16 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 9.22 ‐‐ 7.28 22.3 41 2.31 1.3 3.3 2.97 ‐‐ 61 73 3.4 3.7 0.98 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No SL No No No No No No No No No No SL No No No No No No SL No No No No SL No No No No No No No No SL No No No No No No No No No No No SL No No No No No No No Yes No SL No SL Ratio Boeing Soil Char Level 7.67E‐04 No SL 6.23E‐07 5.08E‐01 6.38E‐05 2.21E‐04 6.38E‐05 1.13E‐03 1.10E‐04 8.87E‐03 4.08E‐05 No SL 5.23E‐03 4.43E‐05 3.19E‐04 1.44E‐02 4.86E‐05 No SL 1.39E‐03 3.19E‐04 1.11E‐04 No SL 1.40E‐04 4.57E‐05 2.49E‐05 4.42E‐04 7.85E‐04 6.15E‐04 1.71E‐03 No SL 1.67E‐05 1.40E‐05 3.00E‐04 2.76E‐04 1.04E‐03 2.51E‐06 9.27E‐04 2.45E‐03 1.73E‐05 1.20E‐05 No SL 1.28E‐03 6.00E‐06 5.00E‐02 1.41E‐03 3.93E‐03 3.93E‐03 8.57E‐03 5.50E+00 No SL No SL ‐‐ No SL No SL 35 2340 No No ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 SCL Basis Suburban Residential RBSL SCL Units RL Units 0.43 mg/kg 5.5 mg/kg Y Y Y 1.57E‐01 Ecological RBSL 3.72E‐04 Ecological RBSL mg/kg mg/kg 5.5 mg/kg 5.5 mg/kg 5.5 mg/kg 0.35 mg/kg Y Y Y Y Y Y No SL No No SL No No No No No No No No No SL 6.37E‐03 No SL 6.60E‐01 5.89E‐01 2.71E‐01 7.73E‐02 4.33E‐01 2.06E‐01 4.35E‐01 2.66E‐01 Background Background Ecological RBSL Ecological RBSL Background Background Background Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.5 5.5 5.5 11 0.55 0.33 5.5 1.1 0.55 7 110 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.5 0.56 1.9 5.4 0.27 0.17 1.1 0.44 0.11 0.33 45 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 0.32 90 No No No No No No No No No No No No No No No No No No No 1.72E‐01 4.20E‐01 3.07E‐01 3.38E‐01 5.40E‐01 2.02E‐01 1.89E‐01 1.57E‐01 1.89E‐01 2.25E‐01 2.18E‐01 3.70E‐01 1.11E‐01 3.15E‐01 3.79E‐02 4.80E‐04 2.18E‐01 6.88E‐02 3.00E‐05 Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 130 1.1 5.5 28 1.1 0.55 0.22 0.22 0.44 0.11 0.44 1.1 0.22 0.22 0.033 4.8 4.8 22 22 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg 130 0.69 1.1 0.75 0.014 0.016 0.0068 0.09 0.055 0.018 0.044 0.088 0.0049 0.0033 0.0061 0.42 0.56 3.6 0.18 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 No No No No No No No No No No No No 9.57E‐03 4.89E‐03 2.09E‐02 1.69E‐03 6.77E‐01 3.02E‐03 4.15E‐04 4.64E‐04 2.42E‐03 1.77E‐03 2.35E‐02 1.60E‐01 Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 22 22 22 22 22 22 22 22 22 22 22 22 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.32 0.51 0.95 0.35 0.5 0.28 0.34 0.18 0.19 0.15 0.16 0.16 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background 0.203 0.305 1.73 1.27 0.203 1.54 0.244 1.11 2.62 0.335 0.203 0.508 0.203 0.305 0.508 0.203 0.203 0.508 0.203 0.508 0.305 0.203 0.305 0.305 0.508 0.203 0.203 0.254 2.03 0.203 0.203 0.203 0.203 0.254 0.203 0.203 0.203 0.203 0.295 0.305 0.305 0.254 0.508 0.508 1.2 1.1 1.1 1.1 1.1 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA 5.5 mg/kg Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg MDL  Units mg/kg Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL 1.02 1.02 5.08 5.08 1.02 5.08 1.02 5.08 5.08 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 2.03 5.08 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 1.02 4.8 5.5 5.5 5.5 5.5 0.1 5.5 MDL Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg RL Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S010 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 13:45 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 EEL EEL CC 1 Soil Boring ELBS1027 ELBS1027S060 Primary Sample 3/26/08 14:00 Soil 5 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027S060 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample Primary Sample 3/26/08 14:00 Soil 3/26/08 14:00 Soil 3/26/08 14:00 Soil Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Analytical Class Analysis  Method Analyte CAS Number Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8015B 8015B 8015B 8015B 9056 Benzo(b)fluoranthene Benzo(ghi)perylene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Bromide 205992 191242 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 108883 156605 10061026 79016 75694 75014 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 24959679 6 In Place Primary Result Inorganics 9056 Chloride 16887006 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium 16984488 NO3N NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 5 5 5 6 In Place 6 In Place 6 In Place Primary Result Primary Result Primary Result Metals Metals Metals 6010B 6010B 6010B Sodium Vanadium Zinc 7440235 7440622 7440666 Page 36 of 108 Result  Value 14 3.5 17 1.5 46 0.89 3.1 0.42 25 37 0.96 1.9 1.9 4.8 1.9 1.9 4.8 1.9 4.8 0.96 1.9 4.8 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.8 48 9.6 4.8 9.6 1.9 4.8 4.8 1.9 4.8 4.8 0.96 1.9 4.8 1.9 4.8 4.8 1.9 1.9 1.9 1.9 0.96 4.8 1.9 9.6 4.8 4.8 4.8 4.8 1.9 4.8 4.8 4.8 1.9 4.8 0.96 1.9 4.8 1.9 1.9 1.9 1.9 1.9 4.8 1.9 2 5.2 5.2 5.2 5.2 0.42 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg 9.5 mg/kg 1.4 1.1 0.36 0.54 12 14000 96 0.86 1.1 24 4.8 36 1800 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 130 mg/kg 39 mg/kg 51 mg/kg Detected Project  Qual  Code mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N J J J J J J J J J J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U U U U U U 9.5 mg/kg N U mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y N N Y Y Y Y N Y Y Y Y U J UJ UJ B, RL changed from 5.4 and  MDL from 2.1 F, result changed from 1.4 and  MDL from 0.88 H H H J A 130 mg/kg 39 mg/kg 51 mg/kg N Y Y Result  in SL Units 0.014 0.0035 0.017 0.0015 0.046 0.00089 0.0031 0.00042 0.025 0.037 0.00096 0.0019 0.0019 0.0048 0.0019 0.0019 0.0048 0.0019 0.0048 0.00096 0.0019 0.0048 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0048 0.048 0.0096 0.0048 0.0096 0.0019 0.0048 0.0048 0.0019 0.0048 0.0048 0.00096 0.0019 0.0048 0.0019 0.0048 0.0048 0.0019 0.0019 0.0019 0.0019 0.00096 0.0048 0.0019 0.0096 0.0048 0.0048 0.0048 0.0048 0.0019 0.0048 0.0048 0.0048 0.0019 0.0048 0.00096 0.0019 0.0048 0.0019 0.0019 0.0019 0.0019 0.0019 0.0048 0.0019 0.002 5.2 5.2 5.2 5.2 5.4 5.4 1.1 5.4 5.4 12 14000 96 0.86 5.4 24 4.8 36 1800 SL Units Validation Note *III Q Q Q $,H $,H $,H $,H $,H $,H $,H $,H Q,$,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $ $ $ $ U J A J A U J F, result changed from 120  and MDL from 64 A Boeing Soil Char Level  (mg/kg) 0.387 7.4 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 3.4 1400 1400 1400 1 ‐‐ Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No No No No SL No No No No No No No Yes No SL Ratio Boeing Soil Char Level 3.62E‐02 4.73E‐04 1.42E‐02 1.33E‐02 8.52E‐04 1.00E‐03 8.01E‐03 2.88E‐05 1.92E‐02 3.08E‐02 3.34E‐04 7.72E‐07 6.60E‐03 2.18E‐05 3.56E‐03 1.01E‐03 6.96E‐04 No SL 4.80E‐04 No SL 6.13E‐04 4.91E‐02 1.83E‐02 1.46E‐05 7.28E‐03 4.33E‐03 5.94E‐04 8.26E‐05 No SL 1.43E‐03 No SL 4.80E+00 4.17E‐04 1.07E‐03 2.09E‐04 1.65E‐02 1.92E‐04 No SL 9.74E‐03 2.09E‐04 1.50E‐03 1.35E‐02 9.05E‐05 No SL 2.59E‐03 1.50E‐03 No SL 2.06E‐04 No SL 1.46E‐03 2.61E‐04 4.30E‐05 1.17E‐04 8.23E‐04 1.18E‐06 No SL 1.62E‐03 1.45E‐03 7.87E‐05 2.60E‐05 3.00E‐04 1.41E‐03 3.00E‐04 5.14E‐04 4.90E‐03 No SL 9.05E‐06 4.36E‐03 4.57E‐03 3.22E‐05 2.23E‐05 No SL 2.38E‐03 2.82E‐05 9.31E‐02 5.88E‐04 3.71E‐03 3.71E‐03 3.71E‐03 5.20E+00 No SL ‐‐ No SL No SL 35 2340 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 No No No SL No No SL No No No No No No No No 1.54E‐01 4.70E‐04 No SL 6.26E‐03 No SL 3.69E‐01 4.71E‐01 1.79E‐01 2.45E‐01 3.99E‐01 1.83E‐01 5.59E‐01 2.39E‐01 754 111.8 153 No No No SCL Basis Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background 1.72E‐01 Background 3.49E‐01 Background 3.33E‐01 Background RL RL Units 22 22 22 22 22 22 22 22 22 22 0.96 1.9 1.9 4.8 1.9 1.9 4.8 1.9 4.8 0.96 1.9 4.8 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 4.8 48 9.6 4.8 9.6 1.9 4.8 4.8 1.9 4.8 4.8 0.96 1.9 4.8 1.9 4.8 4.8 1.9 1.9 1.9 1.9 0.96 4.8 1.9 9.6 4.8 4.8 4.8 4.8 1.9 4.8 4.8 4.8 1.9 4.8 0.96 1.9 4.8 1.9 1.9 1.9 1.9 1.9 4.8 1.9 2 5.2 5.2 5.2 5.2 5.4 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg 9.5 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.4 5.4 5.4 5.4 5.4 11 0.54 0.32 5.4 1.1 0.54 6.8 110 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 130 mg/kg 1.1 mg/kg 5.4 mg/kg MDL 0.16 0.22 0.21 0.27 0.23 0.25 0.27 0.36 0.34 0.19 0.68 0.53 0.66 0.43 0.87 0.56 0.66 0.58 0.54 0.74 0.62 0.56 0.57 0.54 0.67 0.58 0.61 0.62 0.57 0.68 0.6 4.8 1.7 1 3.7 0.52 0.59 0.6 0.52 0.52 0.53 0.48 0.64 0.67 0.62 0.42 0.84 0.63 0.27 0.63 0.67 0.44 0.36 0.78 1.9 1.2 0.85 1.2 0.58 0.49 0.59 0.72 0.76 0.52 0.5 0.43 0.64 0.55 0.77 0.69 0.42 0.45 0.58 0.46 0.3 1.3 1 1 1 1 0.42 MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 9.5 mg/kg Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 130 mg/kg 0.67 mg/kg 1.1 mg/kg Y Y Y Y Y Y Y Y Y 0.88 0.34 0.36 0.54 1.9 5.3 0.26 0.16 1.1 0.43 0.11 0.32 44 Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 EEL EEL EEL CC 1 EEL CC 1 Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample 3/26/08 14:00 Soil 3/26/08 14:00 Soil EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8260B 8260B Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury 1,2,4‐Trichlorobenzene Hexachlorobutadiene 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 120821 87683 5 5 6 In Place 6 In Place Primary Result Primary Result Other SVOCs Other SVOCs 8270C SIM 8270C SIM bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate 117817 85687 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Ethylbenzene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Butylbenzene Tetrachloroethene Page 37 of 108 Result  Value 1.9 0.26 9.5 0.07 7.1 3.4 0.17 15 0.26 0.065 0.2 0.006 4.9 4.9 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Result  in SL Units 1.9 0.26 9.5 0.07 7.1 3.4 0.17 15 0.26 0.065 0.2 0.032 0.0049 0.0049 SL Units Detected Project  Qual  Code Validation Note Boeing Soil Char Level  (mg/kg) 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 10 0.022 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y N N N J J J J 21 ug/kg 0.59 ug/kg 0.021 mg/kg 0.00059 mg/kg N Y U J B,$, result changed from 6.2 0.32 90 No No 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 21 21 0.96 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 0.98 2 2 4.9 2 2 4.9 2 4.9 0.98 2 4.9 2 2 2 2 2 2 2 2 4.9 49 9.8 4.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.021 0.021 0.00096 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.00098 0.002 0.002 0.0049 0.002 0.002 0.0049 0.002 0.0049 0.00098 0.002 0.0049 0.002 0.002 0.002 0.002 0.002 0.002 0.002 0.002 0.0049 0.049 0.0098 0.0049 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U J U U U U U U U U U U U U U U U U U U U U UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ B,$, result changed from 0.41 $ 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 98828 124481 74953 75718 100414 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 98066 127184 9.8 2 4.9 4.9 2 4.9 4.9 0.98 2 4.9 2 4.9 4.9 2 2 2 2 0.98 4.9 2 9.8 4.9 4.9 2 4.9 2 4.9 2 4.9 2 4.9 0.98 2 4.9 2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0098 0.002 0.0049 0.0049 0.002 0.0049 0.0049 0.00098 0.002 0.0049 0.002 0.0049 0.0049 0.002 0.002 0.002 0.002 0.00098 0.0049 0.002 0.0098 0.0049 0.0049 0.002 0.0049 0.002 0.0049 0.002 0.0049 0.002 0.0049 0.00098 0.002 0.0049 0.002 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 1.3 7.28 22.3 41 2.31 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 1.1 0.416 J J J J J U UJ UJ A,Q Q Q Q $,H $,H $ $ $ $ $ $ $ $ $ $ $ $ $ $ $ $ $ $ $ $ $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H B,$,H, Result changed from  4.2 $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H $,H Ratio Boeing Soil Char Level 1.79E‐01 5.20E‐01 3.93E‐01 1.61E‐01 1.69E‐01 1.00E‐01 1.04E‐01 2.34E‐01 2.60E‐01 6.57E‐02 2.63E‐01 3.68E‐02 4.90E‐04 2.23E‐01 SCL Basis Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 27 1.1 0.54 0.22 0.22 0.43 0.11 0.43 1.1 0.22 0.22 0.032 4.9 4.9 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg 0.73 0.013 0.016 0.0066 0.087 0.054 0.017 0.043 0.086 0.0048 0.0032 0.006 0.43 0.57 Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 3.5 ug/kg 0.17 ug/kg Y Y Y Y Y Y 6.56E‐02 Ecological RBSL 6.56E‐06 Ecological RBSL mg/kg mg/kg No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No 9.13E‐03 4.67E‐03 8.73E‐03 1.62E‐03 6.46E‐01 2.88E‐03 3.96E‐04 1.91E‐02 6.36E‐02 9.55E‐03 5.43E‐02 5.43E‐01 5.43E‐02 2.84E‐03 5.43E‐02 1.75E‐02 1.86E‐01 3.89E‐04 2.36E‐02 5.43E‐02 1.44E‐03 1.62E‐02 1.75E‐02 3.41E‐04 8.13E‐07 6.94E‐03 2.23E‐05 3.75E‐03 1.06E‐03 7.10E‐04 No SL 4.90E‐04 No SL 6.45E‐04 5.01E‐02 1.92E‐02 1.54E‐05 7.66E‐03 4.56E‐03 6.25E‐04 8.70E‐05 No SL 1.50E‐03 No SL 4.90E+00 4.26E‐04 1.09E‐03 Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 21 0.98 2 2 4.9 2 2 4.9 2 4.9 0.98 2 4.9 2 2 2 2 2 2 2 2 4.9 49 9.8 4.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.31 0.49 0.9 0.34 0.48 0.27 0.32 0.17 0.18 0.14 0.15 0.15 0.15 0.21 0.14 0.2 0.25 0.22 0.24 0.25 0.34 0.33 0.18 0.7 0.54 0.68 0.44 0.88 0.57 0.68 0.59 0.55 0.75 0.63 0.57 0.58 0.55 0.69 0.59 0.62 0.63 0.58 0.7 0.61 4.9 1.7 1 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No No No No SL No No No No No No SL No No No SL No No SL No No No No No No No SL No No No No No No No No No No SL No No No 2.13E‐04 1.74E‐02 1.96E‐04 No SL 1.03E‐02 2.13E‐04 1.53E‐03 1.38E‐02 9.52E‐05 No SL 2.73E‐03 1.53E‐03 No SL 2.17E‐04 No SL 1.54E‐03 2.75E‐04 4.39E‐05 1.20E‐04 8.66E‐04 1.20E‐06 No SL 1.65E‐03 6.06E‐04 8.03E‐05 2.74E‐05 3.06E‐04 5.88E‐04 3.06E‐04 5.41E‐04 5.00E‐03 No SL 9.52E‐06 4.45E‐03 4.81E‐03 Ecological RBSL Suburban Residential RBSL Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 9.8 2 4.9 4.9 2 4.9 4.9 0.98 2 4.9 2 4.9 4.9 2 2 2 2 0.98 4.9 2 9.8 4.9 4.9 2 4.9 2 4.9 2 4.9 2 4.9 0.98 2 4.9 2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 3.7 0.53 0.6 0.61 0.53 0.53 0.54 0.49 0.66 0.69 0.63 0.43 0.85 0.65 0.27 0.64 0.69 0.45 0.36 0.79 1.9 1.2 0.86 1.3 0.59 0.5 0.6 0.73 0.77 0.53 0.51 0.44 0.66 0.56 0.78 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL 21 ug/kg 21 ug/kg MDL  Units Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1027 ELBS1028 ELBS1028 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1027S060 ELBS1028D010 ELBS1028D010 EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1028 ELBS1028 ELBS1028 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) ELBS1028S010 ELBS1028S010 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/26/08 14:00 3/27/08 11:25 3/27/08 11:25 Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 0 0 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028S010 ELBS1028S010 ELBS1028S010 Field Duplicate Field Duplicate Field Duplicate 3/27/08 11:25 Soil 3/27/08 11:25 Soil 3/27/08 11:25 Soil ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028D010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring ELBS1028 ELBS1028 ELBS1028 ELBS1028S010 ELBS1028S010 ELBS1028S010 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S060 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1028X010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 ELBS1028S010 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 1 1 Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number Result  Value Result  Value  Units Project  Qual  Code VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Metals 8260B 8260B 8260B 8260B 8260B 8260B 9045C 6010B Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride pH Aluminum 108883 156605 10061026 79016 75694 75014 E‐10139 7429905 2 2 2 2 4.9 2 7.19 13400 0 0 0 1 In Place 1 In Place 1 In Place Primary Result Primary Result Primary Result Metals Metals Metals 6010B 6010B 6010B Antimony Boron Potassium 7440360 7440428 7440097 0.656 mg/kg 1.1 mg/kg 2020 mg/kg Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 87.4 9.7 105 0.84 0.16 26 6.7 10.2 9 23.6 0.56 13.7 0.528 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Inorganics Metals 6020 6020 6020 6020 6020 7471A 9045C 6010B Silver Thallium Vanadium Zinc Zirconium Mercury pH Aluminum 7440224 7440280 7440622 7440666 7440677 7439976 E‐10139 7429905 0.211 0.24 43.3 45 3 0.013 7.01 10800 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg Primary Sample Primary Sample Primary Sample 3/27/08 11:25 Soil 3/27/08 11:25 Soil 3/27/08 11:25 Soil 0 0 0 1 In Place 1 In Place 1 In Place Primary Result Primary Result Primary Result Metals Metals Metals 6010B 6010B 6010B Antimony Boron Potassium 7440360 7440428 7440097 0.384 mg/kg 1.04 mg/kg 1720 mg/kg 1.04 mg/kg 5.2 mg/kg 1720 mg/kg N N Y UJ UJ J Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 1 1 1 1 1 1 1 Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 Sodium Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Lithium Molybdenum Nickel Selenium 7440235 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439932 7439987 7440020 7782492 87.6 17.3 112 0.81 0.21 21.2 11.8 11 11.9 20.4 0.51 14.3 0.519 87.6 17.3 112 0.81 0.21 21.2 11.8 11 11.9 20.4 0.51 14.3 1.04 N Y Y Y Y Y Y Y Y Y Y Y N U J Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:35 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/27/08 11:25 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0 0 0 0 0 0 5.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 1 1 1 1 6 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Metals Metals Metals Metals Metals Metals Metals Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 6020 6020 6020 6020 6020 7471A 6020 9045C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 7471A 9045C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Silver Thallium Vanadium Zinc Zirconium Mercury Arsenic pH Aluminum Barium Beryllium Boron Cobalt Copper Lithium Molybdenum Potassium Silver Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Chromium Lead Nickel Selenium Thallium Mercury pH Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Potassium Sodium Vanadium Zinc 7440224 7440280 7440622 7440666 7440677 7439976 7440382 E‐10139 7429905 7440393 7440417 7440428 7440484 7440508 7439932 7439987 7440097 7440224 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440473 7439921 7440020 7782492 7440280 7439976 E‐10139 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7440097 7440235 7440622 7440666 Page 38 of 108 0.208 0.24 46.9 71.4 2.9 0.015 6.7 7.76 27000 115 0.893 12.9 11.1 11 27.8 0.267 2900 1.05 167 53.3 52.6 4.49 0.309 4.9 0.0996 25 9.98 15.3 0.956 0.157 0.011 7.6 14000 91 1 1.1 17 4.5 17 1700 64 35 40 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Validation Note N N N N N N Y Y UJ UJ UJ UJ UJ UJ $,H $,H $,H $,H $,H $,H J 1.06 mg/kg 1.1 mg/kg 2020 mg/kg N Y Y UJ J J 87.4 9.7 105 0.84 0.16 26 6.7 10.2 9 23.6 0.56 13.7 1.06 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y Y N U J *III I, $, MDL and result changed  from 0.328 I *III F, RL CHANGED FROM 15.9  AND MDL CHANGED FROM  4.77 E mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg N Y Y Y Y Y Y Y 0.211 0.24 43.3 45 3 0.013 7.01 10800 0.208 0.24 46.9 71.4 2.9 0.015 6.7 7.76 27000 115 0.893 5.35 11.1 11 27.8 1.07 2900 1.05 167 53.3 52.6 4.49 1.03 4.9 0.0996 25 9.98 15.3 2.06 0.157 0.103 7.6 14000 91 1 5.4 17 4.5 17 1700 130 35 40 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg Detected Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place 0.002 0.002 0.002 0.002 0.0049 0.002 7.19 13400 SL Units In Place In Place In Place In Place In Place In Place In Place In Place Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg Result  in SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y Y Y Y Y Y Y Y Y Y N Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y N Y N Y Y Y Y N Y Y Y Y N Y Y J J J J Q Q, *III E U UJ F, RESULT CHANGED FROM  0.064 AND MDL CHANGED  FROM 0.0422, Q, E J A J B, B, B, B J *III I, $, MDL and result changed  from 0.323 I *III F, RL CHANGED FROM 15.6  AND MDL CHANGED FROM  4.68 E J J J J Q Q, *III E U UJ F, RESULT CHANGED FROM  0.051 AND MDL CHANGED  FROM 0.0416, Q, E J A J B, B, B, B U B B U B, B B B J UJ J J L L B U J UJ B H Q, Q U B U F Boeing Soil Char Level  (mg/kg) 59 85.3 ‐‐ 0.797 170 0.0204 ‐‐ 37900 Exceeds Boeing Soil Char Level No No No SL No No No No SL No 0.5 22 7524 Yes No No 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 Ratio Boeing Soil Char Level 3.39E‐05 2.34E‐05 No SL 2.51E‐03 2.88E‐05 9.80E‐02 No SL 3.54E‐01 SCL Basis Ecological RBSL Suburban Residential RBSL SCL Units RL RL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg 2 2 2 2 4.9 2 0.1 21.2 2.12E+00 MRL 5.00E‐02 Ecological RBSL 2.68E‐01 Background mg/kg mg/kg mg/kg 1.06 mg/kg 5.3 mg/kg 15.9 mg/kg No No No No No No No No No No No No Yes 1.16E‐01 4.01E‐01 5.15E‐01 1.75E‐01 3.68E‐01 4.33E‐01 2.56E‐01 2.43E‐01 2.65E‐01 3.66E‐01 3.41E‐01 2.13E‐01 1.06E+00 Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.99 0.761 111.8 153 10.64 0.87 ‐‐ 37900 No No No No No No No SL No 2.13E‐01 3.15E‐01 3.87E‐01 2.94E‐01 2.82E‐01 1.49E‐02 No SL 2.85E‐01 Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg 0.5 22 7524 Yes No No 2.08E+00 MRL 2.36E‐01 Ecological RBSL 2.29E‐01 Background mg/kg mg/kg mg/kg 754 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 64.4 1.642 64.2 1 No No No No No No No No No No No No Yes 1.16E‐01 7.15E‐01 5.50E‐01 1.69E‐01 4.83E‐01 3.53E‐01 4.51E‐01 2.62E‐01 3.51E‐01 3.17E‐01 3.11E‐01 2.23E‐01 1.04E+00 Background Background Background Ecological RBSL Background Background Background Background Background Background Background Background MRL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.99 0.761 111.8 153 10.64 0.87 24.2 ‐‐ 37900 203.8 4.8 22 26.18 42 64.4 1.642 7524 0.99 754 111.8 153 10.64 0.5 24.2 0.435 60.11 33.9 64.2 1 0.761 0.87 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 7524 754 111.8 153 No No No No No No No No SL No No No No No No No No No Yes No No No No Yes No No No No No Yes No No No SL No No No No No No No No No No No 2.10E‐01 3.15E‐01 4.19E‐01 4.67E‐01 2.73E‐01 1.72E‐02 2.77E‐01 No SL 7.12E‐01 5.64E‐01 1.86E‐01 2.43E‐01 4.24E‐01 2.62E‐01 4.32E‐01 6.52E‐01 3.85E‐01 1.06E+00 2.21E‐01 4.77E‐01 3.44E‐01 4.22E‐01 2.06E+00 2.02E‐01 2.29E‐01 4.16E‐01 2.94E‐01 2.38E‐01 2.06E+00 2.06E‐01 1.18E‐01 No SL 3.69E‐01 4.47E‐01 2.08E‐01 2.45E‐01 2.83E‐01 1.72E‐01 2.64E‐01 2.26E‐01 1.72E‐01 3.13E‐01 2.61E‐01 Ecological RBSL Suburban Residential RBSL Background Background Background Ecological RBSL Background mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Background Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Ecological RBSL Background Background Background Background MRL Background Background Background Background Background MRL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background 87.4 1.06 0.422 0.106 0.211 3.17 1.06 1.06 0.422 10.6 0.106 2.11 1.06 0.211 0.211 10.6 2.07 0.422 0.00984 0.1 20.8 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg 1.04 mg/kg 5.2 mg/kg 15.6 mg/kg 87.6 1.04 0.416 0.104 0.208 0.623 0.208 0.208 0.416 2.08 0.104 0.416 1.04 0.208 0.208 10.4 2.09 0.416 0.0101 1.1 0.01 21.4 0.535 0.535 5.35 0.535 1.07 0.53 1.07 53.5 0.535 107 0.535 2.14 5.35 1.03 2.06 0.257 2.06 1.03 2.06 2.06 0.514 0.103 0.1 11 0.54 0.32 5.4 1.1 0.54 6.8 110 130 1.1 5.4 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL 0.71 0.43 0.46 0.59 0.47 0.3 0.01 7.21 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units mg/kg 0.656 mg/kg 1.06 mg/kg 5.3 mg/kg 87.4 0.317 0.106 0.0211 0.0211 1.06 0.106 0.211 0.106 2.11 0.0211 0.528 0.528 0.211 0.0422 2.11 0.413 0.106 0.00148 0.01 7.08 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg 0.208 0.0416 2.08 0.418 0.104 0.00151 0.331 0.01 3.58 0.0246 0.0727 0.663 0.139 0.214 0.11 0.267 3.54 0.182 37.2 0.171 0.701 1.07 0.309 0.206 0.0987 0.617 0.154 0.586 0.956 0.154 0.011 5.3 0.26 0.16 1.1 0.43 0.11 0.32 44 64 0.67 1.1 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg N Y N N N N N N Y N N N N Y N N N N N N N N N N 0.384 mg/kg 1.04 mg/kg 5.2 mg/kg 87.6 0.312 0.104 0.0208 0.0208 0.208 0.0208 0.0416 0.104 0.416 0.0208 0.104 0.519 Y Y Y Y Y Y N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N Y N Y N Y N N N Y N Y N Y N Y Y Y Y Y Y N N Y Y N Y Y Y Y N Y Y N N N N Y N N N Y N N Y Y N N N N Y N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS1029 ELBS13 ELBS13 ELBS13 ELBS13 ELBS13 ELBS13 ELBS13 ELBS14 ELBS14 ELBS14 ELBS14 ELBS14 ELBS14 ELBS14 ELBS1400 ELBS1400 ELBS1401 ELBS1402 ELBS1402 ELBS1402 ELBS1402 ELBS1402 ELBS1402 ELBS1402 ELBS1402 ELBS1403 ELBS1403 ELBS1403 ELBS1403 ELBS1403 ELBS1405 ELBS1409 ELBS1409 ELBS1410 ELBS1410 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 ELBS1029X010 MT825 MT825 MT825 MT825 MT825 MT825 MT825 MT826 MT826 MT826 MT826 MT826 MT826 MT826 ELBS1400D01 ELBS1400S01 ELBS1401S01 ELBS1402S01 ELBS1402S01 ELBS1402S01 ELBS1402S01 ELBS1402X01 ELBS1402X01 ELBS1402X01 ELBS1402X01 ELBS1403D01 ELBS1403D01 ELBS1403S01 ELBS1403S01 ELBS1403S02 ELBS1405S01 ELBS1409S01 ELBS1409S01 ELBS1410S01 ELBS1410S01 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 Sample ID ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS1029S010 ELBS13S01 ELBS13S01 ELBS13S01 ELBS13S01 ELBS13S01 ELBS13S01 ELBS13S01 ELBS14S01 ELBS14S01 ELBS14S01 ELBS14S01 ELBS14S01 ELBS14S01 ELBS14S01 ELBS1400S01 ELBS1402S01 ELBS1402S01 ELBS1402S01 ELBS1402S01 ELBS1403S01 ELBS1403S01 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 3/24/08 13:40 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 9/17/03 0:00 5/23/08 10:56 5/23/08 10:56 5/23/08 11:17 5/30/08 13:15 5/30/08 13:15 5/30/08 13:15 5/30/08 13:15 5/30/08 13:15 5/30/08 13:15 5/30/08 13:15 5/30/08 13:15 5/23/08 12:43 5/23/08 12:43 5/23/08 12:43 5/23/08 12:43 5/23/08 12:48 6/2/08 12:12 5/23/08 13:34 5/23/08 13:34 5/27/08 8:18 5/27/08 8:18 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 3.5 0.5 4.5 4.5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 4 1 5 5 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Analysis  Method 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 9045C 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 6020 6020 6020 6010B 6020 6020 6020 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 1613B 1613B 1613B 9045C 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A Analyte Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury pH Aluminum Barium Beryllium Boron Cobalt Copper Lithium Molybdenum Potassium Silver Sodium Vanadium Zinc Zirconium Arsenic Cadmium Chromium Lead Nickel Selenium Thallium Mercury Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Arsenic Arsenic Arsenic Aluminum Arsenic Barium Silver Aluminum Barium Silver Arsenic Barium Silver Barium Silver Chromium Arsenic Arsenic Barium Arsenic Barium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal pH 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene Page 39 of 108 CAS Number 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 E‐10139 7429905 7440393 7440417 7440428 7440484 7440508 7439932 7439987 7440097 7440224 7440235 7440622 7440666 7440677 7440382 7440439 7440473 7439921 7440020 7782492 7440280 7439976 12674112 11104282 11141165 53469219 12672296 11097691 11096825 12674112 11104282 11141165 53469219 12672296 11097691 11096825 7440382 7440382 7440382 7429905 7440382 7440393 7440224 7429905 7440393 7440224 7440382 7440393 7440224 7440393 7440224 7440473 7440382 7440382 7440393 7440382 7440393 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal E‐10139 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 Result  Value 1.1 0.25 5 0.085 7.1 7.1 0.43 10 0.3 0.061 0.23 0.0081 7.52 20700 109 0.825 7.36 5.2 10.9 23.2 0.271 2450 0.184 97.3 40.7 50.7 4.16 7.24 0.298 24.3 11.4 15.1 1.01 0.28 0.011 53 53 53 53 53 53 53 53 53 53 53 53 53 53 7.8 7.4 5 19000 5.7 130 0.058 23800 136 0.696 5.15 93 0.045 100 0.039 28 5.6 24 130 3.9 83.8 6.72 5.52 8.81 7.7 23.2 257 1.63 1.23 2.82 1.4 9.27 0.798 6.93 4.51 1.54 1.16 0.923 1.22 0.269 76.7 517 34.5 67.2 65.5 4220 21.1 56.9 24 6.6 350 350 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg Result  in SL Units SL Units 27 mg/kg 0.25 mg/kg 5 mg/kg 0.085 mg/kg 7.1 mg/kg 7.1 mg/kg 0.43 mg/kg 10 mg/kg 0.3 mg/kg 0.061 mg/kg 0.23 mg/kg 0.0081 mg/kg 7.52 ph Units 20700 mg/kg 109 mg/kg 0.825 mg/kg 5.41 mg/kg 5.2 mg/kg 10.9 mg/kg 23.2 mg/kg 1.08 mg/kg 2450 mg/kg 0.541 mg/kg 108 mg/kg 40.7 mg/kg 50.7 mg/kg 4.16 mg/kg 7.24 mg/kg 0.298 mg/kg 24.3 mg/kg 11.4 mg/kg 15.1 mg/kg 2.16 mg/kg 0.28 mg/kg 0.103 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 0.053 mg/kg 7.8 mg/kg 7.4 mg/kg 5 mg/kg 19000 mg/kg 5.7 mg/kg 130 mg/kg 0.058 mg/kg 23800 mg/kg 136 mg/kg 0.696 mg/kg 5.15 mg/kg 93 mg/kg 0.045 mg/kg 100 mg/kg 0.039 mg/kg 28 mg/kg 5.6 mg/kg 24 mg/kg 130 mg/kg 3.9 mg/kg 83.8 mg/kg 0.00000672 mg/kg 0.00000552 mg/kg 0.00000881 mg/kg 7.7 ph Units 0.0000232 mg/kg 0.000257 mg/kg 0.00000163 mg/kg 0.00000123 mg/kg 0.00000282 mg/kg 0.0000014 mg/kg 0.00000927 mg/kg 0.000000798 mg/kg 0.00000693 mg/kg 0.00000451 mg/kg 0.00000154 mg/kg 0.00000116 mg/kg 0.000000923 mg/kg 0.00000122 mg/kg 0.000000269 mg/kg 0.00000572 mg/kg 0.000517 mg/kg 0.00000572 mg/kg 0.00000572 mg/kg 0.0000655 mg/kg 0.00422 mg/kg 0.00000572 mg/kg 0.00000572 mg/kg 0.00000114 mg/kg 0.00000114 mg/kg 0.35 mg/kg 0.35 mg/kg Detected N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y N Y N N Y Y Y Y Y Y Y Y N Y N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N Y Y N N N N N N Project  Qual  Code U J Validation Note F B J J J Q, Q J Q, Q B U B U Q, Q, B U U J J J U J UJ U U U U U U U U U U U U U U F Q, Q Q Q Q, Q Q, Q Q, Q B,H Q, Q, B Q J Q, Q J Q J J J Q J Q Q, Q J J J J J J J J J J UJ UJ UJ UJ UJ UJ UJ U U F, B F, B F, B F, B F, B F, B F, B F, B B F, B F, B F, B F, B B F, B M, F F M, F M, F, B F, B F, B M, F E, M, F M, F, B M, F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 10.64 Yes 2.54E+00 Background 0.5 No 5.00E‐01 MRL 24.2 No 2.07E‐01 Background 0.435 No 1.95E‐01 Background 42 No 1.69E‐01 Background 33.9 No 2.09E‐01 Background 1.642 No 2.62E‐01 Background 64.2 No 1.56E‐01 Background 1 No 3.00E‐01 MRL 0.99 No 6.16E‐02 Ecological RBSL 0.761 No 3.02E‐01 Suburban Residential RBSL 0.87 No 9.31E‐03 Ecological RBSL ‐‐ No SL No SL 37900 No 5.46E‐01 Background 203.8 No 5.35E‐01 Background 4.8 No 1.72E‐01 Ecological RBSL 22 No 2.46E‐01 Ecological RBSL 26.18 No 1.99E‐01 Background 42 No 2.60E‐01 Background 64.4 No 3.60E‐01 Background 1.642 No 6.58E‐01 Background 7524 No 3.26E‐01 Background 0.99 No 5.46E‐01 Ecological RBSL 754 No 1.43E‐01 Background 111.8 No 3.64E‐01 Background 153 No 3.31E‐01 Background 10.64 No 3.91E‐01 Background 24.2 No 2.99E‐01 Background 0.435 No 6.85E‐01 Background 60.11 No 4.04E‐01 Background 33.9 No 3.36E‐01 Background 64.2 No 2.35E‐01 Background 1 Yes 2.16E+00 MRL 0.761 No 3.68E‐01 Suburban Residential RBSL 0.87 No 1.18E‐01 Ecological RBSL 0.12 No 4.42E‐01 Ecological RBSL 0.18 No 2.94E‐01 Ecological RBSL 0.082 No 6.46E‐01 Ecological RBSL 0.043 Yes 1.23E+00 Ecological RBSL 0.017 Yes 3.12E+00 MRL 0.039 Yes 1.36E+00 Ecological RBSL 0.025 Yes 2.12E+00 Ecological RBSL 0.12 No 4.42E‐01 Ecological RBSL 0.18 No 2.94E‐01 Ecological RBSL 0.082 No 6.46E‐01 Ecological RBSL 0.043 Yes 1.23E+00 Ecological RBSL 0.017 Yes 3.12E+00 MRL 0.039 Yes 1.36E+00 Ecological RBSL 0.025 Yes 2.12E+00 Ecological RBSL 24.2 No 3.22E‐01 Background 24.2 No 3.06E‐01 Background 24.2 No 2.07E‐01 Background 37900 No 5.01E‐01 Background 24.2 No 2.36E‐01 Background 203.8 No 6.38E‐01 Background 0.99 No 5.86E‐02 Ecological RBSL 37900 No 6.28E‐01 Background 203.8 No 6.67E‐01 Background 0.99 No 7.03E‐01 Ecological RBSL 24.2 No 2.13E‐01 Background 203.8 No 4.56E‐01 Background 0.99 No 4.55E‐02 Ecological RBSL 203.8 No 4.91E‐01 Background 0.99 No 3.94E‐02 Ecological RBSL 60.11 No 4.66E‐01 Background 24.2 No 2.31E‐01 Background 24.2 No 9.92E‐01 Background 203.8 No 6.38E‐01 Background 24.2 No 1.61E‐01 Background 203.8 No 4.11E‐01 Background 0.0000057 Yes 1.18E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.56E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.80E‐01 Ecological RBSL 0.3 Yes 1.17E+00 MRL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 27 1.1 0.54 0.22 0.22 0.43 0.11 0.43 1.1 0.22 0.22 0.032 0.01 21.6 0.541 0.541 5.41 0.541 1.08 0.54 1.08 54.1 0.541 108 0.541 2.16 5.41 2.16 0.271 2.16 1.08 2.16 2.16 0.541 0.103 53 53 53 53 53 53 53 53 53 53 53 53 53 53 0.62 0.64 0.62 11 0.65 0.54 0.22 21.6 0.541 0.541 1.06 0.56 0.22 0.55 0.22 1.1 1.17 0.66 0.55 1.11 2.23 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.74 0.013 0.016 0.0066 0.088 0.054 0.017 0.043 0.087 0.0048 0.0032 0.006 0.01 3.62 0.0249 0.0736 0.671 0.141 0.216 0.11 0.271 3.58 0.184 37.7 0.173 0.709 1.08 0.216 0.104 0.649 0.162 0.617 1.01 0.162 0.011 53 53 53 53 53 53 53 53 53 53 53 53 53 53 0.052 0.054 0.052 1.7 0.055 0.076 0.022 3.63 0.433 0.184 0.106 0.079 0.023 0.078 0.022 0.083 0.351 0.056 0.078 0.334 0.557 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.01 5.72 5.72 5.72 5.72 5.72 5.72 5.72 5.72 5.72 5.72 5.72 5.72 5.72 1.14 1.14 5.72 5.72 5.72 5.72 11.4 11.4 5.72 5.72 1.14 1.14 350 350 pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg 0.01 0.0397 0.161 0.0526 0.0541 0.0791 0.0534 0.0834 0.0637 0.0827 0.0539 0.127 0.055 0.0536 0.0969 0.0624 0.0452 0.161 0.0563 0.0816 0.0415 0.0969 0.0538 0.127 0.0969 0.0624 120 120 pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N N N Y N Y Y N Y N Y Y N N Y Y Y N Y N N Y Y Y Y Y Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N Y N N Y Y Y N N Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N N Y N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000D001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 9045C 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal pH 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran Page 40 of 108 CAS Number 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal E‐10139 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 Result  Value 690 350 690 350 350 350 350 350 350 460 350 2300 2300 350 350 350 2 2 41 20 100 14 20 28 2900 2900 0.12 32.4 0.46 35 0.46 0.83 8.7 0.21 21500 112 0.778 9.99 25.1 8.06 20.1 408 4010 95.6 46.7 63.5 4.44 0.304 6.55 0.439 17.3 16.5 0.564 19.7 0.148 0.163 0.405 20 20 20 20 20 20 20 35 20 2 1.1 4.5 0.96 0.96 0.73 20 0.96 2 2 0.96 2 2 2 2.1 0.96 0.96 0.96 2 7.7 38 5.51 4.27 6.81 7.99 19.8 208 1.56 1.11 2.19 0.99 7.57 0.663 5.86 4.4 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.69 mg/kg 0.35 mg/kg 0.69 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.46 mg/kg 0.35 mg/kg 2.3 mg/kg 2.3 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.002 mg/kg 0.002 mg/kg 0.041 mg/kg 0.02 mg/kg 0.1 mg/kg 0.014 mg/kg 0.02 mg/kg 0.028 mg/kg 2.9 mg/kg 2.9 mg/kg 2.3 mg/kg 32.4 mg/kg 1.2 mg/kg 35 mg/kg 1.2 mg/kg 0.83 mg/kg 5.8 mg/kg 0.57 mg/kg 21500 mg/kg 112 mg/kg 0.778 mg/kg 9.99 mg/kg 25.1 mg/kg 8.06 mg/kg 20.1 mg/kg 408 mg/kg 4010 mg/kg 95.6 mg/kg 46.7 mg/kg 63.5 mg/kg 4.44 mg/kg 0.304 mg/kg 6.55 mg/kg 0.439 mg/kg 17.3 mg/kg 16.5 mg/kg 0.564 mg/kg 19.7 mg/kg 0.148 mg/kg 0.163 mg/kg 0.405 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.035 mg/kg 0.02 mg/kg 0.002 mg/kg 0.0011 mg/kg 0.0045 mg/kg 0.00096 mg/kg 0.00096 mg/kg 0.00073 mg/kg 0.02 mg/kg 0.00096 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00096 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.0021 mg/kg 0.00096 mg/kg 0.00096 mg/kg 0.00096 mg/kg 0.002 mg/kg 0.0077 mg/kg 0.038 mg/kg 0.00000551 mg/kg 0.00000427 mg/kg 0.00000681 mg/kg 7.99 ph Units 0.0000198 mg/kg 0.000208 mg/kg 0.00000156 mg/kg 0.00000111 mg/kg 0.00000219 mg/kg 0.00000099 mg/kg 0.00000757 mg/kg 0.000000663 mg/kg 0.00000586 mg/kg 0.0000044 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N N Y N N N Y N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U J U J U U Validation Note L L L F Q Q F Q, Q, B J B Q, Q J Q Q, Q F J J J J J J J J J J J U U U U U U U Q, Q, Q Q, Q Q, Q Q, Q Q, Q Q Q Q Q Q, Q U U J U U U J U U U U U U U U U U U U U U U J J J J J J F, B F, B F, B F, B F, B F, B F, B F, B B F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.17E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 4.18E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.17E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 4.17E‐04 Ecological RBSL 0.55 No 3.64E‐03 Ecological RBSL 1.1 No 3.73E‐02 Ecological RBSL 6.2 No 3.23E‐03 Ecological RBSL 39 No 2.56E‐03 Ecological RBSL 14 No 1.00E‐03 Ecological RBSL 0.79 No 2.53E‐02 Ecological RBSL 0.18 No 1.56E‐01 Ecological RBSL 3.3 No 8.79E‐01 MRL 3.3 No 8.79E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 3.43E‐02 Ecological RBSL 2340 No 1.50E‐02 Ecological RBSL ‐‐ No SL No SL 863.2 No 9.62E‐04 Background ‐‐ No SL No SL 0.5 Yes 1.14E+00 MRL 37900 No 5.67E‐01 Background 203.8 No 5.50E‐01 Background 4.8 No 1.62E‐01 Ecological RBSL 22 No 4.54E‐01 Ecological RBSL 60.11 No 4.18E‐01 Background 26.18 No 3.08E‐01 Background 64.4 No 3.12E‐01 Background 723 No 5.64E‐01 Background 7524 No 5.33E‐01 Background 754 No 1.27E‐01 Background 111.8 No 4.18E‐01 Background 153 No 4.15E‐01 Background 10.64 No 4.17E‐01 Background 0.5 No 6.08E‐01 MRL 24.2 No 2.71E‐01 Background 0.435 Yes 1.01E+00 Background 42 No 4.12E‐01 Background 33.9 No 4.87E‐01 Background 1.642 No 3.43E‐01 Background 64.2 No 3.07E‐01 Background 1 No 1.48E‐01 MRL 0.99 No 1.65E‐01 Ecological RBSL 0.761 No 5.32E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.67E‐01 Ecological RBSL 0.18 No 1.11E‐01 Ecological RBSL 0.082 No 2.44E‐01 Ecological RBSL 0.043 No 4.65E‐01 Ecological RBSL 0.017 Yes 1.18E+00 MRL 0.039 No 8.97E‐01 Ecological RBSL 0.025 No 8.00E‐01 Ecological RBSL 0.0051 No 3.92E‐01 Ecological RBSL 0.004164 No 2.64E‐01 Background 0.006101 No 7.38E‐01 Background 0.0348 No 2.76E‐02 Suburban Residential RBSL 0.073 No 1.32E‐02 Ecological RBSL 0.394 No 1.85E‐03 Suburban Residential RBSL 1.1 No 1.82E‐02 Ecological RBSL 0.067 No 1.43E‐02 Ecological RBSL 0.013 No 1.54E‐01 Ecological RBSL 0.23 No 8.70E‐03 Ecological RBSL 0.22 No 4.36E‐03 Ecological RBSL 0.22 No 9.09E‐03 Ecological RBSL 0.0079 No 2.53E‐01 Ecological RBSL 0.0092 No 2.17E‐01 Ecological RBSL 0.0086 No 2.44E‐01 Ecological RBSL 0.075 No 1.28E‐02 Ecological RBSL 0.087 No 1.10E‐02 Ecological RBSL 0.0017 No 5.65E‐01 MRL 0.0328 No 6.10E‐02 Suburban Residential RBSL 2.5 No 3.08E‐03 Ecological RBSL 0.493 No 7.71E‐02 Suburban Residential RBSL 0.0000057 No 9.67E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.21E+01 Background No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 690 350 690 350 350 350 350 350 350 460 350 2300 2300 350 350 350 2 2 41 20 100 14 20 28 2900 2900 2.3 11.5 1.2 5.3 1.2 5.8 5.8 0.57 11.4 0.572 0.286 5.72 0.858 0.572 2.3 0.572 57.2 57.2 0.572 2.29 5.72 0.229 0.458 0.114 0.229 0.229 0.114 0.458 0.458 0.114 0.114 20 20 20 20 20 20 20 20 20 2 2 4.5 0.96 0.96 1.2 20 0.96 2 2 0.96 2 2 2 2.1 0.96 0.96 0.96 2 7.7 38 0.01 5.24 5.24 5.24 5.24 5.24 5.24 5.24 5.24 5.24 5.24 MDL  Units RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 230 120 230 120 120 230 290 170 230 290 120 1700 1700 140 120 180 0.94 0.86 14 7.1 51 4.6 10 10 880 860 0.12 2.3 0.46 2 0.46 0.12 1.8 0.21 8.83 0.0378 0.0767 0.95 0.101 0.103 0.63 0.095 15.5 19.1 0.126 0.229 0.95 0.0778 0.0961 0.0527 0.167 0.0167 0.0572 0.176 0.114 0.0229 0.0343 3.8 3.8 4.1 5.3 9.2 3.8 3.8 3.8 5.6 0.38 0.38 4.5 0.38 0.2 0.35 4.6 0.21 1.4 0.38 0.25 0.53 0.57 0.71 0.38 0.2 0.35 0.36 1.1 2 13 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.01 0.0386 0.124 0.0451 0.0436 0.0644 0.0446 0.0697 0.0496 0.0676 0.0531 Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y pH Units Y ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N N Y N N N N N N N N N N N N N N Y N N Y N N N N N N N N N N N N N N N Y N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A Analyte 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Page 41 of 108 CAS Number 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 Result  Value 1.25 0.966 0.903 1.08 0.147 68 440 26.4 58.5 67.9 2680 19.8 25.7 23.6 4.8 320 320 630 320 630 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.8 1.8 38 18 94 13 18 25 940 2600 0.1 34.1 0.7 25 0.42 0.64 4.9 0.18 16700 92 0.598 7.68 23.8 6.99 15.7 385 3180 78.2 35.6 52.9 3.19 0.281 5.28 0.471 15.1 16.3 0.61 21 0.169 0.175 0.204 18 18 18 18 18 18 18 98 18 1.8 1.8 8 0.87 0.87 1 18 0.87 2.3 1.8 0.87 1.8 1.8 1.1 1.9 0.87 0.87 0.87 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00000125 mg/kg 0.000000966 mg/kg 0.000000903 mg/kg 0.00000108 mg/kg 0.00000105 mg/kg 0.00000524 mg/kg 0.00044 mg/kg 0.00000524 mg/kg 0.0000585 mg/kg 0.0000679 mg/kg 0.00268 mg/kg 0.00000524 mg/kg 0.00000524 mg/kg 0.00000105 mg/kg 0.00000105 mg/kg 0.32 mg/kg 0.32 mg/kg 0.63 mg/kg 0.32 mg/kg 0.63 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.42 mg/kg 0.32 mg/kg 2.1 mg/kg 2.1 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.038 mg/kg 0.018 mg/kg 0.094 mg/kg 0.013 mg/kg 0.018 mg/kg 0.025 mg/kg 0.94 mg/kg 2.6 mg/kg 2.1 mg/kg 34.1 mg/kg 1 mg/kg 25 mg/kg 1 mg/kg 0.64 mg/kg 5.2 mg/kg 0.51 mg/kg 16700 mg/kg 92 mg/kg 0.598 mg/kg 7.68 mg/kg 23.8 mg/kg 6.99 mg/kg 15.7 mg/kg 385 mg/kg 3180 mg/kg 78.2 mg/kg 35.6 mg/kg 52.9 mg/kg 3.19 mg/kg 0.281 mg/kg 5.28 mg/kg 0.471 mg/kg 15.1 mg/kg 16.3 mg/kg 0.61 mg/kg 21 mg/kg 0.169 mg/kg 0.175 mg/kg 0.204 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.098 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.008 mg/kg 0.00087 mg/kg 0.00087 mg/kg 0.001 mg/kg 0.018 mg/kg 0.00087 mg/kg 0.0023 mg/kg 0.0018 mg/kg 0.00087 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0011 mg/kg 0.0019 mg/kg 0.00087 mg/kg 0.00087 mg/kg 0.00087 mg/kg Detected Y Y Y Y N N Y N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N Y N Y N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N N Y Y N N N N N N N N N N Y N N N N Project  Qual  Code J J J U UJ UJ UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ J U U U J U J U U Validation Note F, B F, B F, B B F, B M, F F M, F F, B F, B F, B M, F E, M, F M, F, B M, F L L L F Q Q F Q, Q, B J B Q, Q J Q Q, Q F J J J J J J J J J J J U U U U U U U U U U U U U U U U U U U J U U U U Q, Q, Q Q, Q Q, Q Q, Q Q, Q Q Q Q Q Q, Q Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 0.075 0.087 0.0017 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL Yes No No No No No No No No No No No No No No No Yes No No No No No No No No SL No SL No No No No Yes Yes No No No Yes No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.48E‐01 1.07E+00 No SL No SL No SL No SL 1.07E+00 No SL No SL No SL No SL 3.82E‐03 No SL No SL No SL 1.07E+00 No SL No SL 3.75E‐04 3.27E‐03 3.45E‐02 2.90E‐03 2.41E‐03 9.29E‐04 2.28E‐02 1.39E‐01 2.85E‐01 7.88E‐01 No SL No SL 2.86E‐02 1.07E‐02 No SL 7.41E‐04 No SL 1.02E+00 4.41E‐01 4.51E‐01 1.25E‐01 3.49E‐01 3.96E‐01 2.67E‐01 2.44E‐01 5.33E‐01 4.23E‐01 1.04E‐01 3.18E‐01 3.46E‐01 3.00E‐01 5.62E‐01 2.18E‐01 1.08E+00 3.60E‐01 4.81E‐01 3.71E‐01 3.27E‐01 1.69E‐01 1.77E‐01 2.68E‐01 No SL No SL 1.50E‐01 1.00E‐01 2.20E‐01 4.19E‐01 1.06E+00 2.51E+00 7.20E‐01 3.53E‐01 4.32E‐01 1.31E+00 2.50E‐02 1.19E‐02 2.54E‐03 1.64E‐02 1.30E‐02 1.77E‐01 7.83E‐03 3.95E‐03 8.18E‐03 2.28E‐01 1.20E‐01 2.21E‐01 1.16E‐02 1.00E‐02 5.12E‐01 SCL Basis Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.24 5.24 5.24 1.05 1.05 5.24 5.24 5.24 5.24 10.5 10.5 5.24 5.24 1.05 1.05 320 320 630 320 630 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.8 1.8 38 18 94 13 18 25 2600 2600 2.1 10.5 1 4.4 1 5.2 5.2 0.51 10.4 0.521 0.261 5.21 0.782 0.521 2.1 0.521 52.1 52.1 0.521 2.08 5.21 0.208 0.417 0.104 0.208 0.208 0.104 0.417 0.417 0.104 0.104 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.87 0.87 1 18 0.87 2.3 1.8 0.87 1.8 1.8 1.8 1.9 0.87 0.87 0.87 RL Units MDL ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.111 0.0419 0.0483 0.0931 0.0555 0.0416 0.124 0.0448 0.0673 0.0285 0.0685 0.0505 0.111 0.0931 0.0555 110 110 210 110 210 110 110 210 260 160 210 260 110 1600 1600 130 110 160 0.86 0.78 13 6.5 46 4.2 9.4 9.4 790 780 0.1 2.1 0.42 1.9 0.42 0.1 1.7 0.18 8.04 0.0344 0.0698 0.865 0.0917 0.0938 0.57 0.0865 14.1 17.4 0.115 0.208 0.865 0.0709 0.0875 0.0479 0.152 0.0152 0.0521 0.161 0.104 0.0208 0.0313 3.4 3.4 3.8 4.8 8.3 3.4 3.4 3.4 5.1 0.35 0.35 0.35 0.35 0.18 0.31 4.2 0.19 2.3 0.35 0.23 0.71 0.92 0.35 0.35 0.18 0.31 0.55 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N Y N Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y Y N N N N N N N N N N N N N N N Y N N Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000S001 ELBS2000S001 ELBS2000S001 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S002 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/18/13 8:15 6/18/13 8:15 6/18/13 8:15 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:25 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Analysis  Method 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 7199 8315A 1613B 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A Analyte Mirex Methoxychlor Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene Page 42 of 108 CAS Number 2385855 72435 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 Result  Value 2 7 35 5.4 5.4 6.4 5.4 19 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 0.72 1.8 1.4 0.74 1.8 1.7 1.8 1.8 1.8 1.8 1.1 1.4 1.6 4.4 0.3 2.2 0.00822 0.00822 0.0535 0.055 6.4 6.4 6.4 6.4 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 0.298 4.12 0.0548 0.0718 0.0783 0.0679 0.181 0.175 0.31 0.193 0.0478 0.127 0.0198 0.0341 1.01 8 0.95 2.67 0.886 41 0.899 1.31 0.359 0.154 320 320 640 320 640 320 320 Result  Value  Units ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.002 mg/kg 0.007 mg/kg 0.035 mg/kg 5.4 mg/kg 5.4 mg/kg 6.4 mg/kg 5.4 mg/kg 19 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00072 mg/kg 0.0018 mg/kg 0.0014 mg/kg 0.00074 mg/kg 0.0018 mg/kg 0.0017 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0011 mg/kg 0.0014 mg/kg 0.0016 mg/kg 0.0044 mg/kg 0.43 mg/kg 2.2 mg/kg 8.22E‐09 mg/kg 8.22E‐09 mg/kg 5.35E‐08 mg/kg 0.00000127 mg/kg 6.4 mg/kg 6.4 mg/kg 6.4 mg/kg 6.4 mg/kg 13 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.00000636 mg/kg 0.00000412 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000127 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.0000127 mg/kg 0.000041 mg/kg 0.00000636 mg/kg 0.00000636 mg/kg 0.00000127 mg/kg 0.00000127 mg/kg 0.32 mg/kg 0.32 mg/kg 0.64 mg/kg 0.32 mg/kg 0.64 mg/kg 0.32 mg/kg 0.32 mg/kg Detected N N N N N Y N Y N N N N N N N N N N N N Y N Y Y N Y N Y N N Y Y Y N N N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N Project  Qual  Code Validation Note U U U U U U U U U U U U U U U U U U J U J J U J U U U J J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J UJ UJ UJ UJ UJ U UJ UJ UJ UJ U U UJ UJ UJ UJ U UJ UJ UJ UJ U U U U U U U F F L B F F L B, F F, B M, F, B M, F, B M, F, B M, F, B M, F F, B M, B M, F, B M, F, B M, F, B F, B F M, F, B M, F, B M, F, B M, F, B B, F F, B M, F, B M, F, B M, F, B M, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.0328 No 6.10E‐02 Suburban Residential RBSL 2.5 No 2.80E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 1400 No 3.86E‐03 1400 No 3.86E‐03 1400 No 4.57E‐03 1 Yes 5.40E+00 1400 No 1.36E‐02 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 1.46E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 5.45E‐03 Ecological RBSL 2.2 No 8.18E‐04 Ecological RBSL 0.387 No 1.86E‐03 Suburban Residential RBSL 0.0387 No 4.65E‐02 Suburban Residential RBSL 0.387 No 3.62E‐03 Suburban Residential RBSL 7.4 No 1.00E‐04 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 1.2 No 1.42E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 3.33E‐05 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 14.6 No 7.53E‐05 Suburban Residential RBSL 1.3 No 1.08E‐03 Ecological RBSL 1.2 No 1.33E‐03 Ecological RBSL 0.5 No 8.80E‐03 Ecological RBSL 1.29 No 3.33E‐01 Suburban Residential RBSL 43 No 5.12E‐02 Ecological RBSL 0.0000057 No 1.44E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 9.50E‐02 Background ‐‐ No SL No SL 1400 No 4.57E‐03 1400 No 4.57E‐03 1400 No 4.57E‐03 1 Yes 6.40E+00 1400 No 9.29E‐03 0.32 No 7.19E‐02 Ecological RBSL 90 No 2.56E‐04 Ecological RBSL 2.3 No 1.00E‐02 Ecological RBSL 4.5 No 5.11E‐03 Ecological RBSL 0.11 No 2.09E‐01 Ecological RBSL 13 No 1.77E‐03 Ecological RBSL 0.0325 No 6.46E‐02 Suburban Residential RBSL 7.29 No 2.88E‐04 Suburban Residential RBSL 53 No 3.96E‐05 Ecological RBSL 1.1 No 1.91E‐03 Ecological RBSL 0.33 No 6.36E‐03 Ecological RBSL 2.2 No 9.55E‐04 Ecological RBSL 0.387 No 5.43E‐03 Suburban Residential RBSL 0.0387 No 5.43E‐02 Suburban Residential RBSL 0.387 No 5.43E‐03 Suburban Residential RBSL 7.4 No 2.84E‐04 Ecological RBSL 0.387 No 5.43E‐03 Suburban Residential RBSL 1.2 No 1.75E‐03 Ecological RBSL 0.113 No 1.86E‐02 Suburban Residential RBSL 54 No 3.89E‐05 Ecological RBSL 0.89 No 2.36E‐03 Ecological RBSL 0.387 No 5.43E‐03 Suburban Residential RBSL 14.6 No 1.44E‐04 Suburban Residential RBSL 1.3 No 1.62E‐03 Ecological RBSL 1.2 No 1.75E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.48E‐01 Ecological RBSL 0.3 Yes 1.07E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ 0.3 Yes 1.07E+00 MRL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA 2 7 35 5.4 5.4 5.4 5.4 11 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.4 0.43 2.2 ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 2 1.8 12 2.2 2.2 2.2 2.2 4.3 6.4 6.4 6.4 6.4 6.4 6.4 0.72 0.72 0.72 0.72 0.36 0.36 0.72 0.72 0.72 0.72 0.72 0.36 0.72 0.72 0.72 0.72 0.72 0.72 0.72 2.3 0.15 1.3 ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 1.27 6.4 6.4 6.4 6.4 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 6.36 6.36 6.36 6.36 6.36 6.36 6.36 6.36 6.36 6.36 6.36 6.36 6.36 1.27 6.36 6.36 6.36 6.36 12.7 12.7 6.36 6.36 1.27 1.27 320 320 640 320 640 320 320 ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.055 2.6 2.6 2.6 2.6 5.1 7.6 7.6 7.6 7.6 7.6 7.6 0.84 0.84 0.84 0.84 0.42 0.42 0.84 0.84 0.84 0.84 0.84 0.42 0.84 0.84 0.84 0.84 0.84 0.84 0.84 0.0141 0.0395 0.02 0.016 0.0343 0.0157 0.0366 0.0178 0.0343 0.0221 0.0366 0.0149 0.0198 0.0341 0.0166 0.0395 0.016 0.035 0.0329 0.0383 0.0208 0.0366 0.0312 0.0341 110 110 210 110 210 110 110 ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N Y N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N Y Y N N N Y Y Y N Y Y Y N Y N N Y N N Y N Y N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date Matrix  Type 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Lab Repeat Analysis Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7199 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Hexavalent Chromium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran Page 43 of 108 CAS Number 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 18540299 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 Result  Value 320 320 320 320 430 320 2100 2100 320 320 320 2.2 2.2 46 22 120 15 22 31 3200 3200 1.3 42.2 5.3 2.3 0.51 1.3 73 5.1 0.23 22500 80.8 0.745 9.09 28.3 6.49 29.5 263 2540 412 45.6 67.2 5.69 0.318 9.52 0.222 18.9 10.1 0.244 25.1 0.125 0.0863 0.414 0.34 22 22 22 22 22 22 22 22 22 2.2 2.2 2.2 1.1 1.1 1.3 22 1.1 2.2 2.2 1.1 2.2 2.2 2.2 2.3 1.1 0.58 1.1 2.2 8.5 42 2.5 0.00846 0.00846 0.0539 0.345 0.398 4.08 0.226 0.147 0.212 0.133 0.454 0.264 0.396 0.325 0.118 0.18 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.43 mg/kg 0.32 mg/kg 2.1 mg/kg 2.1 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.0022 mg/kg 0.0022 mg/kg 0.046 mg/kg 0.022 mg/kg 0.12 mg/kg 0.015 mg/kg 0.022 mg/kg 0.031 mg/kg 3.2 mg/kg 3.2 mg/kg 2.6 mg/kg 42.2 mg/kg 1.3 mg/kg 5.8 mg/kg 1.3 mg/kg 6.4 mg/kg 73 mg/kg 0.0051 mg/kg 0.63 mg/kg 22500 mg/kg 80.8 mg/kg 0.745 mg/kg 9.09 mg/kg 28.3 mg/kg 6.49 mg/kg 29.5 mg/kg 263 mg/kg 2540 mg/kg 412 mg/kg 45.6 mg/kg 67.2 mg/kg 5.69 mg/kg 0.318 mg/kg 9.52 mg/kg 0.222 mg/kg 18.9 mg/kg 10.1 mg/kg 0.244 mg/kg 25.1 mg/kg 0.499 mg/kg 0.0863 mg/kg 0.414 mg/kg 0.53 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.0022 mg/kg 0.0022 mg/kg 0.0022 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0013 mg/kg 0.022 mg/kg 0.0011 mg/kg 0.0022 mg/kg 0.0022 mg/kg 0.0011 mg/kg 0.0022 mg/kg 0.0022 mg/kg 0.0022 mg/kg 0.0023 mg/kg 0.0011 mg/kg 0.00058 mg/kg 0.0011 mg/kg 0.0022 mg/kg 0.0085 mg/kg 0.042 mg/kg 2.5 mg/kg 8.46E‐09 mg/kg 8.46E‐09 mg/kg 5.39E‐08 mg/kg 0.000000991 mg/kg 0.00000495 mg/kg 0.00000408 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N Y N N N N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N Y Y Y N N Y N N N N N N N N N N Project  Qual  Code U U U U U U U U U U U U U U U U U U UJ U U U U U U UJ Validation Note L L L F Q F U U Q, Q, B J B Q, Q J Q Q, Q F J J J J J J J J U J J U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U J U U U U U UJ UJ U U U Q, Q, Q Q, Q Q, Q Q, Q Q, Q Q Q Q Q Q, Q B D, B F, B F, B F, B F, B F, B F, B F, B F, B, M B, M F, B F, B F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL 110 No 3.91E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.07E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 4.58E‐04 Ecological RBSL 0.55 No 4.00E‐03 Ecological RBSL 1.1 No 4.18E‐02 Ecological RBSL 6.2 No 3.55E‐03 Ecological RBSL 39 No 3.08E‐03 Ecological RBSL 14 No 1.07E‐03 Ecological RBSL 0.79 No 2.78E‐02 Ecological RBSL 0.18 No 1.72E‐01 Ecological RBSL 3.3 No 9.70E‐01 MRL 3.3 No 9.70E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 3.71E‐02 Ecological RBSL 2340 No 2.48E‐03 Ecological RBSL ‐‐ No SL No SL 863.2 No 7.41E‐03 Background ‐‐ No SL No SL 0.5 No 1.02E‐02 Ecological RBSL 0.5 Yes 1.26E+00 MRL 37900 No 5.94E‐01 Background 203.8 No 3.96E‐01 Background 4.8 No 1.55E‐01 Ecological RBSL 22 No 4.13E‐01 Ecological RBSL 60.11 No 4.71E‐01 Background 26.18 No 2.48E‐01 Background 64.4 No 4.58E‐01 Background 723 No 3.64E‐01 Background 7524 No 3.38E‐01 Background 754 No 5.46E‐01 Background 111.8 No 4.08E‐01 Background 153 No 4.39E‐01 Background 10.64 No 5.35E‐01 Background 0.5 No 6.36E‐01 MRL 24.2 No 3.93E‐01 Background 0.435 No 5.10E‐01 Background 42 No 4.50E‐01 Background 33.9 No 2.98E‐01 Background 1.642 No 1.49E‐01 Background 64.2 No 3.91E‐01 Background 1 No 4.99E‐01 MRL 0.99 No 8.72E‐02 Ecological RBSL 0.761 No 5.44E‐01 Suburban Residential RBSL 1.29 No 4.11E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.83E‐01 Ecological RBSL 0.18 No 1.22E‐01 Ecological RBSL 0.082 No 2.68E‐01 Ecological RBSL 0.043 No 5.12E‐01 Ecological RBSL 0.017 Yes 1.29E+00 MRL 0.039 No 5.64E‐01 Ecological RBSL 0.025 No 8.80E‐01 Ecological RBSL 0.0051 No 4.31E‐01 Ecological RBSL 0.004164 No 5.28E‐01 Background 0.006101 No 3.61E‐01 Background 0.0348 No 3.16E‐02 Suburban Residential RBSL 0.073 No 1.51E‐02 Ecological RBSL 0.394 No 3.30E‐03 Suburban Residential RBSL 1.1 No 2.00E‐02 Ecological RBSL 0.067 No 1.64E‐02 Ecological RBSL 0.013 No 1.69E‐01 Ecological RBSL 0.23 No 9.57E‐03 Ecological RBSL 0.22 No 5.00E‐03 Ecological RBSL 0.22 No 1.00E‐02 Ecological RBSL 0.0079 No 2.78E‐01 Ecological RBSL 0.0092 No 2.39E‐01 Ecological RBSL 0.0086 No 2.67E‐01 Ecological RBSL 0.075 No 1.47E‐02 Ecological RBSL 0.087 No 6.67E‐03 Ecological RBSL 0.0017 No 6.47E‐01 MRL 0.0328 No 6.71E‐02 Suburban Residential RBSL 2.5 No 3.40E‐03 Ecological RBSL 0.493 No 8.52E‐02 Suburban Residential RBSL 43 No 5.81E‐02 Ecological RBSL 0.0000057 No 1.48E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 9.57E‐02 Background ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL 320 320 320 320 430 320 2100 2100 320 320 320 2.2 2.2 46 22 120 15 22 31 3200 3200 2.6 12.8 1.3 5.8 1.3 6.4 12.8 5.1 0.63 12.5 0.623 0.312 6.23 0.935 0.623 2.5 0.623 62.3 62.3 0.623 2.49 6.23 0.249 0.499 0.125 0.249 0.249 0.125 0.499 0.499 0.125 0.125 0.53 22 22 22 22 22 22 22 22 22 2.2 2.2 2.2 1.1 1.1 1.3 22 1.1 2.2 2.2 1.1 2.2 2.2 2.2 2.3 1.1 1.1 1.1 2.2 8.5 42 2.5 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 210 270 160 210 270 110 1600 1600 130 110 160 1 0.96 15 7.9 56 5.1 12 12 970 960 1.3 2.6 0.51 2.3 0.51 1.3 4.1 2.7 0.23 9.61 0.0411 0.0835 1.03 0.11 0.112 0.69 0.103 16.8 20.8 0.137 0.249 1.03 0.0847 0.105 0.0573 0.182 0.0182 0.0623 0.192 0.125 0.0249 0.0374 0.19 4.2 4.2 4.6 5.8 10 4.2 4.2 4.2 6.2 0.42 0.42 0.42 0.42 0.22 0.38 5.1 0.23 0.42 0.42 0.28 0.42 0.42 0.42 0.42 0.22 0.38 0.24 0.42 2.2 14 1.5 0.991 4.95 4.95 4.95 4.95 4.95 4.95 4.95 4.95 4.95 4.95 4.95 4.95 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N Y Y N N Y N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N Y Y Y Y N N N Y Y Y Y Y N N Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date Matrix  Type 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8015B 8015B 8015B 8015B 6010B 6850 9012B 9056 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7196A 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans sym‐Trinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 4‐Amino‐2,6‐Dinitrotoluene HMX 1,3‐Dinitrobenzene 3‐Nitrotoluene Nitrobenzene Nitroglycerin 2‐Nitrotoluene PETN 4‐Nitrotoluene RDX Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Phosphorus Perchlorate Cyanides Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Antimony Barium Boron Calcium Chromium Cobalt Iron Manganese Potassium Silver Sodium Strontium Tin Titanium Vanadium Zinc Aluminum Arsenic Beryllium Cadmium Copper Lead Lithium Magnesium Molybdenum Nickel Selenium Thallium Zirconium Hexavalent Chromium bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Page 44 of 108 CAS Number 57117314 1746016 51207319 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 99354 118967 6629294 121142 59229753 606202 35572782 19406510 2691410 99650 99081 98953 55630 88722 78115 99990 121824 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 7723140 14797730 57125 24959679 16887006 16984488 NO3 NO2 14265442 14808798 7440360 7440393 7440428 7440702 7440473 7440484 7439896 7439965 7440097 7440224 7440235 7440246 7440315 7440326 7440622 7440666 7429905 7440382 7440417 7440439 7440508 7439921 7439932 7439954 7439987 7440020 7782492 7440280 7440677 18540299 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 Result  Value 0.264 0.0913 0.279 1.08 43.8 13.4 1.17 3.08 1.34 1.08 1.08 0.161 1.68 150 150 2000 150 2000 150 150 150 150 150 150 150 1000 150 500 150 150 150 6.1 6.1 6.1 6.1 122 6.1 6.1 6.1 1220 1220 2.01 2.01 2.01 2.01 275 2.41 0.0944 0.818 67.4 10 0.44 0.403 0.818 153 0.531 73.1 8.97 13200 18.9 4.63 20500 174 2020 0.146 372 41.3 0.337 954 34.7 52.7 19000 4.06 0.632 0.172 9.89 5.93 22.4 5840 0.236 14 0.397 0.251 3.32 0.188 189 189 189 189 189 189 189 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00000495 mg/kg 0.000000991 mg/kg 0.000000991 mg/kg 0.00000991 mg/kg 0.0000438 mg/kg 0.0000134 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.00000495 mg/kg 0.000000991 mg/kg 0.00000168 mg/kg 0.15 mg/kg 0.15 mg/kg 2 mg/kg 0.15 mg/kg 2 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 1 mg/kg 0.15 mg/kg 0.5 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.0061 mg/kg 0.0061 mg/kg 0.0061 mg/kg 0.0061 mg/kg 0.122 mg/kg 0.0061 mg/kg 0.0061 mg/kg 0.0061 mg/kg 1.22 mg/kg 1.22 mg/kg 2.01 mg/kg 2.01 mg/kg 2.01 mg/kg 2.01 mg/kg 275 mg/kg 0.00241 mg/kg 0.283 mg/kg 2.44 mg/kg 67.4 mg/kg 10 mg/kg 0.44 mg/kg 1.22 mg/kg 2.44 mg/kg 153 mg/kg 0.531 mg/kg 73.1 mg/kg 8.97 mg/kg 13200 mg/kg 18.9 mg/kg 4.63 mg/kg 20500 mg/kg 174 mg/kg 2020 mg/kg 0.146 mg/kg 372 mg/kg 41.3 mg/kg 1.12 mg/kg 954 mg/kg 34.7 mg/kg 52.7 mg/kg 19000 mg/kg 4.06 mg/kg 0.632 mg/kg 0.172 mg/kg 9.89 mg/kg 5.93 mg/kg 22.4 mg/kg 5840 mg/kg 0.236 mg/kg 14 mg/kg 1.2 mg/kg 0.251 mg/kg 3.32 mg/kg 0.47 mg/kg 0.189 mg/kg 0.189 mg/kg 0.189 mg/kg 0.189 mg/kg 0.189 mg/kg 0.189 mg/kg 0.189 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg Detected N N N N Y Y N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N Y Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N N N N N N N N N N N N N N N Project  Qual  Code U U U UJ UJ UJ UJ UJ UJ UJ Validation Note F, B F, B B M, F, B F, B F, B F, B, M F, B, M F, B, M F, B, M F, B, M F, B, M F, B U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U L F J U U F J J Q J U F J B J U J U U U U U U U U U U U U U U U U U F F Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ 110 0.92 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 1400 1400 1400 1 ‐‐ 0.5 0.5 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 203.8 22 ‐‐ 60.11 26.18 ‐‐ 723 7524 0.99 754 1210 31 1865 111.8 153 37900 24.2 4.8 0.435 42 33.9 64.4 ‐‐ 1.642 64.2 1 0.761 10.64 1.29 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No No SL No SL No SL No SL No No SL No No No SL No SL No SL No SL No SL No SL No No SL No No No No No No No No No No No No No Yes No SL No No No SL No SL No No No SL No No SL Yes No No No SL No No No SL No No No No No No No No No No No No No No No No No SL No No Yes No No No No No No No Yes No Yes No No No No No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 5.00E‐01 No SL No SL No SL No SL 5.00E‐01 No SL 1.36E‐03 1.63E‐01 No SL No SL No SL No SL No SL No SL 5.00E‐01 No SL 1.27E‐03 1.11E‐02 5.55E‐03 9.84E‐04 3.13E‐03 4.36E‐04 7.72E‐03 3.39E‐02 3.70E‐01 3.70E‐01 1.44E‐03 1.44E‐03 1.44E‐03 2.01E+00 No SL 4.82E‐03 5.66E‐01 No SL No SL 2.86E‐01 1.88E‐04 No SL 2.83E‐03 No SL 1.06E+00 3.59E‐01 4.08E‐01 No SL 3.14E‐01 1.77E‐01 No SL 2.41E‐01 2.68E‐01 1.47E‐01 4.93E‐01 3.41E‐02 3.61E‐02 5.12E‐01 3.10E‐01 3.44E‐01 5.01E‐01 1.68E‐01 1.32E‐01 3.95E‐01 2.35E‐01 1.75E‐01 3.48E‐01 No SL 1.44E‐01 2.18E‐01 1.20E+00 3.30E‐01 3.12E‐01 3.64E‐01 5.91E‐01 2.10E‐03 8.22E‐02 4.20E‐02 1.72E+00 1.45E‐02 5.82E+00 5.19E‐04 7.13E‐05 3.44E‐03 1.15E‐02 1.72E‐03 9.77E‐03 9.77E‐02 9.77E‐03 5.11E‐04 SCL Basis MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL MRL Ecological RBSL Ecological RBSL Background MRL Background Ecological RBSL Background Background Background Background Ecological RBSL Background Ecological RBSL Ecological RBSL Background Background Background Background Background Ecological RBSL Background Background Background Background Background Background MRL Suburban Residential RBSL Background Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 4.95 0.991 0.991 9.91 9.91 4.95 4.95 4.95 4.95 4.95 4.95 0.991 0.991 150 150 2000 150 2000 150 150 150 150 150 150 150 1000 150 500 150 150 150 6.1 6.1 6.1 6.1 122 6.1 6.1 6.1 1220 1220 2.01 2.01 2.01 2.01 16.9 2.41 0.283 2.44 2.44 1.22 1.22 1.22 2.44 4.88 1.12 0.562 5.62 28.1 0.562 0.562 28.1 1.12 28.1 0.562 28.1 0.562 1.12 0.562 0.562 1.12 120 1.2 0.12 0.241 0.241 0.482 2.41 72.3 0.241 0.482 1.2 0.482 0.482 0.47 189 189 189 189 189 189 189 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 50 50 500 50 660 50 50 50 50 50 50 50 250 50 82.5 50 50 50 2.03 2.03 2.03 2.03 42.7 2.44 2.76 2.03 281 244 0.664 0.664 0.664 0.664 5.62 0.602 0.0944 0.818 0.818 0.403 0.403 0.403 0.818 1.62 0.371 0.112 1.12 9 0.169 0.169 9 0.225 7.2 0.112 7.87 0.112 0.337 0.112 0.112 0.45 36.1 0.241 0.0241 0.0241 0.0795 0.12 0.482 24.1 0.0723 0.12 0.397 0.0723 0.12 0.188 56.6 56.6 56.6 56.6 56.6 56.6 56.6 0.944 0.944 0.944 0.944 0.944 0.944 0.944 0.944 0.944 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y Y N N N Y N N Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y N N Y N N Y N N Y N Y Y Y N N N N N N N N N Y N N N N N Y N N N N N N N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S003SP ELBS2000S004 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 ELBS2000S003 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:35 6/18/13 8:40 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 10 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Analysis  Method 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 9012B Analyte Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1268 Aroclor 5432 Aroclor 5442 Aroclor 5460 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1262 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan I Endosulfan II Endosulfan sulfate Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Methoxychlor Mirex Toxaphene Formaldehyde Antimony DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Cyanides Page 45 of 108 CAS Number 207089 218019 53703 206440 86737 193395 91203 85018 129000 11100144 63496311 12642238 11126424 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 72548 72559 50293 309002 319846 319857 57749 319868 60571 959988 33213659 1031078 72208 7421934 53494705 58899 76448 1024573 72435 2385855 8001352 50000 7440360 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 57125 Result  Value 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 4.05 20.3 20.3 20.3 4.05 4.05 4.05 4.05 4.05 4.05 4.05 4.05 1.62 1.62 1.62 0.81 0.81 0.81 10.1 0.81 1.62 0.81 1.62 1.62 1.62 1.62 1.62 0.81 0.81 0.81 8.1 0.81 20.2 2.4 0.109 0.21 0.226 0.498 1.27 19.9 0.192 0.195 0.204 0.206 0.696 0.249 0.579 0.47 0.133 0.155 0.163 0.0814 0.0302 3.59 41.1 2.73 4.51 3.96 343 2.87 9.2 3.13 0.235 290 290 580 290 580 290 290 290 290 290 290 390 290 1900 1900 290 290 290 1.7 1.7 36 17 90 12 17 24 2500 2500 0.18 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Result  in SL Units SL Units 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00378 mg/kg 0.00405 mg/kg 0.0203 mg/kg 0.0203 mg/kg 0.0203 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00405 mg/kg 0.00162 mg/kg 0.00162 mg/kg 0.00162 mg/kg 0.00081 mg/kg 0.00081 mg/kg 0.00081 mg/kg 0.0101 mg/kg 0.00081 mg/kg 0.00162 mg/kg 0.00081 mg/kg 0.00162 mg/kg 0.00162 mg/kg 0.00162 mg/kg 0.00162 mg/kg 0.00162 mg/kg 0.00081 mg/kg 0.00081 mg/kg 0.00081 mg/kg 0.0081 mg/kg 0.00081 mg/kg 0.0202 mg/kg 2.4 mg/kg 0.253 mg/kg 0.00000021 mg/kg 0.000000226 mg/kg 0.000000498 mg/kg 0.00000127 mg/kg 0.0000199 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.000000204 mg/kg 0.000000206 mg/kg 0.000000696 mg/kg 0.00000504 mg/kg 0.000000579 mg/kg 0.00000047 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.00000101 mg/kg 0.00000101 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.00000396 mg/kg 0.000343 mg/kg 0.00000504 mg/kg 0.00000504 mg/kg 0.00000101 mg/kg 0.00000101 mg/kg 0.29 mg/kg 0.29 mg/kg 0.58 mg/kg 0.29 mg/kg 0.58 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.39 mg/kg 0.29 mg/kg 1.9 mg/kg 1.9 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.036 mg/kg 0.017 mg/kg 0.09 mg/kg 0.012 mg/kg 0.017 mg/kg 0.024 mg/kg 2.5 mg/kg 2.5 mg/kg 0.49 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y N N Y Y Y N Y Y N N N N N N N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ UJ J UJ U J J J U J J U UJ U U UJ UJ UJ UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U Validation Note S S S, L S S S S S S S S S S, L S S S S S S S S H Q, Q F, B F, B M, F, B B, F B B F, B B, F F, B F, B F, B M, F, B F, B B M, F, B M, F M, F M, F M, F, B F, B F, B M, F M, F M, B M, F L L L Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.387 No 9.77E‐03 Suburban Residential RBSL 1.2 No 3.15E‐03 Ecological RBSL 0.113 No 3.35E‐02 Suburban Residential RBSL 54 No 7.00E‐05 Ecological RBSL 0.89 No 4.25E‐03 Ecological RBSL 0.387 No 9.77E‐03 Suburban Residential RBSL 14.6 No 2.59E‐04 Suburban Residential RBSL 1.3 No 2.91E‐03 Ecological RBSL 1.2 No 3.15E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.05 No 4.06E‐01 MRL 0.12 No 3.38E‐02 Ecological RBSL 0.18 No 2.25E‐02 Ecological RBSL 0.082 No 4.94E‐02 Ecological RBSL 0.043 No 9.42E‐02 Ecological RBSL 0.017 No 2.38E‐01 MRL 0.039 No 1.04E‐01 Ecological RBSL 0.025 No 1.62E‐01 Ecological RBSL ‐‐ No SL No SL 0.0051 No 3.18E‐01 Ecological RBSL 0.004164 No 3.89E‐01 Background 0.006101 No 2.66E‐01 Background 0.0348 No 2.33E‐02 Suburban Residential RBSL 0.073 No 1.11E‐02 Ecological RBSL 0.394 No 2.06E‐03 Suburban Residential RBSL 1.1 No 9.18E‐03 Ecological RBSL 0.067 No 1.21E‐02 Ecological RBSL 0.013 No 1.25E‐01 Ecological RBSL 0.22 No 3.68E‐03 Ecological RBSL 0.22 No 7.36E‐03 Ecological RBSL 0.23 No 7.04E‐03 Ecological RBSL 0.0079 No 2.05E‐01 Ecological RBSL 0.0092 No 1.76E‐01 Ecological RBSL 0.0086 No 1.88E‐01 Ecological RBSL 0.075 No 1.08E‐02 Ecological RBSL 0.087 No 9.31E‐03 Ecological RBSL 0.0017 No 4.76E‐01 MRL 2.5 No 3.24E‐03 Ecological RBSL 0.0328 No 2.47E‐02 Suburban Residential RBSL 0.493 No 4.10E‐02 Suburban Residential RBSL 43 No 5.58E‐02 Ecological RBSL 0.5 No 5.06E‐01 MRL 0.0000057 No 3.68E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 8.85E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.15E‐01 Ecological RBSL 0.3 No 9.67E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 9.67E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL 110 No 3.55E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 9.67E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.54E‐04 Ecological RBSL 0.55 No 3.09E‐03 Ecological RBSL 1.1 No 3.27E‐02 Ecological RBSL 6.2 No 2.74E‐03 Ecological RBSL 39 No 2.31E‐03 Ecological RBSL 14 No 8.57E‐04 Ecological RBSL 0.79 No 2.15E‐02 Ecological RBSL 0.18 No 1.33E‐01 Ecological RBSL 3.3 No 7.58E‐01 MRL 3.3 No 7.58E‐01 MRL 0.5 No 9.80E‐01 MRL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 3.78 4.05 20.3 20.3 20.3 4.05 4.05 4.05 4.05 4.05 4.05 4.05 4.05 1.62 1.62 1.62 0.81 0.81 0.81 10.1 0.81 1.62 0.81 1.62 1.62 1.62 1.62 1.62 0.81 0.81 0.81 8.1 0.81 20.2 2.4 0.253 5.04 5.04 5.04 5.04 5.04 5.04 5.04 5.04 5.04 5.04 5.04 5.04 5.04 1.01 1.01 5.04 5.04 5.04 5.04 10.1 10.1 5.04 5.04 1.01 1.01 290 290 580 290 580 290 290 290 290 290 290 390 290 1900 1900 290 290 290 1.7 1.7 36 17 90 12 17 24 2500 2500 0.49 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg MDL 0.944 0.944 0.944 0.944 0.944 0.944 0.566 0.944 0.944 1.35 4.05 4.05 4.05 1.35 1.35 1.35 1.35 1.35 1.35 1.35 1.35 0.405 0.405 0.405 0.202 0.202 0.202 2.02 0.202 0.405 0.202 0.405 0.405 0.405 0.405 0.405 0.202 0.202 0.202 2.02 0.202 6.74 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.109 mg/kg 0.0202 0.0575 0.0244 0.0264 0.0446 0.0273 0.0487 0.0293 0.0469 0.0303 0.0422 0.0258 0.0281 0.0457 0.0301 0.0222 0.0575 0.0272 0.0467 0.0248 0.0373 0.0292 0.0422 0.0457 0.0301 97 97 190 97 190 97 97 190 240 150 190 240 97 1500 1500 120 97 150 0.82 0.75 12 6.2 44 4 9 9 760 750 0.18 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S001 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S002 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:30 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:40 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Analysis  Method 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 6850 7199 8315A 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM Analyte Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Page 46 of 108 CAS Number 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 67630 117817 85687 84662 Result  Value 12400 119 0.35 4.6 14.6 5.6 15.3 302 3920 213 41.7 49.7 3.64 0.104 4.65 0.127 14.1 7.5 0.35 10.1 0.102 0.034 0.249 17 17 17 17 17 17 17 16 17 1.7 0.89 4 0.84 0.84 1 19 0.84 1.7 1.7 0.84 1.7 1.7 1.7 1.8 0.84 0.84 0.84 1.3 6.8 34 5.9 5.9 15 5.9 70 1.2 21 21 21 21 21 21 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 0.82 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.2 1.2 4.7 0.51 4.7 0 0 0 5.2 5.2 5.2 5.2 10 1.1 19 19 19 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg Result  in SL Units 12400 119 0.35 5.11 14.6 5.6 15.3 302 3920 213 41.7 49.7 3.64 0.204 4.65 0.127 14.1 7.5 0.35 10.1 0.409 0.034 0.249 0.017 0.017 0.017 0.017 0.017 0.017 0.017 0.016 0.017 0.0017 0.00089 0.004 0.00084 0.00084 0.001 0.019 0.00084 0.0017 0.0017 0.00084 0.0017 0.0017 0.0017 0.0018 0.00084 0.00084 0.00084 0.0013 0.0068 0.034 5.9 5.9 15 5.9 70 1.2 0.021 0.021 0.021 0.021 0.021 0.021 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.00082 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 1.2 1.2 0.0047 0.47 4.7 0 0 0 5.2 5.2 5.2 5.2 10 1.1 0.019 0.019 0.019 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y N N N N N N N Y N N Y Y N N N N N N N N N N N N N N N Y N N N N Y N Y N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note Q, Q, B U J F, B Q, Q J Q Q, Q J U J J J J J J U J J U U U U U U U J U U J Q, Q, Q, B Q, Q Q, Q Q, Q Q, Q, F Q Q Q Q Q, Q U U U U U U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U F F L B F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 37900 No 3.27E‐01 Background 203.8 No 5.84E‐01 Background 4.8 No 7.29E‐02 Ecological RBSL 22 No 2.32E‐01 Ecological RBSL 60.11 No 2.43E‐01 Background 26.18 No 2.14E‐01 Background 64.4 No 2.38E‐01 Background 723 No 4.18E‐01 Background 7524 No 5.21E‐01 Background 754 No 2.82E‐01 Background 111.8 No 3.73E‐01 Background 153 No 3.25E‐01 Background 10.64 No 3.42E‐01 Background 0.5 No 4.08E‐01 MRL 24.2 No 1.92E‐01 Background 0.435 No 2.92E‐01 Background 42 No 3.36E‐01 Background 33.9 No 2.21E‐01 Background 1.642 No 2.13E‐01 Background 64.2 No 1.57E‐01 Background 1 No 4.09E‐01 MRL 0.99 No 3.43E‐02 Ecological RBSL 0.761 No 3.27E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.42E‐01 Ecological RBSL 0.18 No 9.44E‐02 Ecological RBSL 0.082 No 2.07E‐01 Ecological RBSL 0.043 No 3.95E‐01 Ecological RBSL 0.017 No 1.00E+00 MRL 0.039 No 4.10E‐01 Ecological RBSL 0.025 No 6.80E‐01 Ecological RBSL 0.0051 No 3.33E‐01 Ecological RBSL 0.004164 No 2.14E‐01 Background 0.006101 No 6.56E‐01 Background 0.0348 No 2.41E‐02 Suburban Residential RBSL 0.073 No 1.15E‐02 Ecological RBSL 0.394 No 2.54E‐03 Suburban Residential RBSL 1.1 No 1.73E‐02 Ecological RBSL 0.067 No 1.25E‐02 Ecological RBSL 0.013 No 1.31E‐01 Ecological RBSL 0.23 No 7.39E‐03 Ecological RBSL 0.22 No 3.82E‐03 Ecological RBSL 0.22 No 7.73E‐03 Ecological RBSL 0.0079 No 2.15E‐01 Ecological RBSL 0.0092 No 1.85E‐01 Ecological RBSL 0.0086 No 2.09E‐01 Ecological RBSL 0.075 No 1.12E‐02 Ecological RBSL 0.087 No 9.66E‐03 Ecological RBSL 0.0017 No 4.94E‐01 MRL 0.0328 No 3.96E‐02 Suburban Residential RBSL 2.5 No 2.72E‐03 Ecological RBSL 0.493 No 6.90E‐02 Suburban Residential RBSL 1400 No 4.21E‐03 1400 No 4.21E‐03 1400 No 1.07E‐02 1 Yes 5.90E+00 1400 No 5.00E‐02 ‐‐ No SL No SL 0.32 No 6.56E‐02 Ecological RBSL 90 No 2.33E‐04 Ecological RBSL 2.3 No 9.13E‐03 Ecological RBSL 4.5 No 4.67E‐03 Ecological RBSL 0.11 No 1.91E‐01 Ecological RBSL 13 No 1.62E‐03 Ecological RBSL 0.0325 No 5.85E‐02 Suburban Residential RBSL 7.29 No 2.61E‐04 Suburban Residential RBSL 53 No 3.58E‐05 Ecological RBSL 1.1 No 1.73E‐03 Ecological RBSL 0.33 No 5.76E‐03 Ecological RBSL 2.2 No 8.64E‐04 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 0.0387 No 4.91E‐02 Suburban Residential RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 7.4 No 2.57E‐04 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 1.2 No 6.83E‐04 Ecological RBSL 0.113 No 1.68E‐02 Suburban Residential RBSL 54 No 3.52E‐05 Ecological RBSL 0.89 No 2.13E‐03 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 14.6 No 1.30E‐04 Suburban Residential RBSL 1.3 No 1.46E‐03 Ecological RBSL 1.2 No 1.58E‐03 Ecological RBSL No SL ‐‐ No SL ‐‐ No SL No SL 0.5 No 9.40E‐03 Ecological RBSL 1.29 No 3.64E‐01 Suburban Residential RBSL 43 No 1.09E‐01 Ecological RBSL 0.0000057 No 0.00E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 0.00E+00 Background 1400 No 3.71E‐03 1400 No 3.71E‐03 1400 No 3.71E‐03 1 Yes 5.20E+00 1400 No 7.14E‐03 ‐‐ No SL No SL 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 10.2 0.511 0.255 5.11 0.766 0.511 2 0.511 51.1 51.1 0.511 2.04 5.11 0.204 0.409 0.102 0.204 0.204 0.102 0.409 0.409 0.102 0.102 17 17 17 17 17 17 17 17 17 1.7 1.7 1.7 0.84 0.84 1 19 0.84 1.7 1.7 0.84 1.7 1.7 1.7 1.8 0.84 0.84 0.84 1.7 6.8 34 5.9 5.9 5.9 5.9 12 1.2 21 21 21 21 21 21 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.2 1.2 4.7 0.47 4.7 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ug/kg mg/kg mg/kg 7.88 0.0337 0.0684 0.848 0.0899 0.0919 0.56 0.0848 13.8 17.1 0.112 0.204 0.848 0.0695 0.0858 0.047 0.149 0.0149 0.0511 0.157 0.102 0.0204 0.0306 3.4 3.4 3.7 4.7 8.1 3.4 3.4 3.4 5 0.34 0.34 0.34 0.34 0.17 0.31 19 0.18 1 0.34 0.22 0.34 0.39 0.34 0.34 0.17 0.31 0.4 0.34 1.7 11 2.3 2.3 2.3 2.3 4.7 0.24 7 7 7 7 7 7 0.77 0.77 0.77 0.77 0.39 0.39 0.77 0.77 0.77 0.77 0.77 0.39 0.77 0.77 0.77 0.77 0.77 0.77 0.77 0.24 0.24 2.5 0.17 2.8 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ug/kg mg/kg mg/kg 5.2 5.2 5.2 5.2 10 1.1 19 19 19 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg 2.1 2.1 2.1 2.1 4.2 0.21 6.2 6.2 6.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 7199 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A Analyte Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Hexavalent Chromium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC Page 47 of 108 CAS Number 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 18540299 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 Result  Value 19 19 19 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.1 1.1 0.0332 0.0714 0.0409 0.0408 0.0182 0.0281 0.0233 0.0564 0.0626 0.016 0.0403 0.0356 0.0311 0.0225 0.0297 0.105 0.222 0.19 0.527 0.089 0.28 0.169 0.327 0.137 0.127 320 320 630 320 630 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.8 1.4 38 18 94 13 18 25 2600 2600 0.1 2.8 0.61 2.8 0.42 0.18 6.2 43 0.19 0.29 18 18 18 18 18 18 18 5.5 18 1.8 1.8 0.98 0.88 0.88 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 1.1 mg/kg 1.1 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000104 mg/kg 0.00000104 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.0000104 mg/kg 0.0000104 mg/kg 0.00000522 mg/kg 0.00000522 mg/kg 0.00000104 mg/kg 0.00000104 mg/kg 0.32 mg/kg 0.32 mg/kg 0.63 mg/kg 0.32 mg/kg 0.63 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.42 mg/kg 0.32 mg/kg 2.1 mg/kg 2.1 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.0018 mg/kg 0.0014 mg/kg 0.038 mg/kg 0.018 mg/kg 0.094 mg/kg 0.013 mg/kg 0.018 mg/kg 0.025 mg/kg 2.6 mg/kg 2.6 mg/kg 2.1 mg/kg 2.8 mg/kg 0.61 mg/kg 2.8 mg/kg 1 mg/kg 0.18 mg/kg 5.2 mg/kg 0.043 mg/kg 0.52 mg/kg 0.42 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0055 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00098 mg/kg 0.00088 mg/kg 0.00088 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N Y Y Y N Y N Y N N N N N N N N N Y N N N Y N N Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U UJ UJ UJ U UJ UJ UJ U U U UJ UJ UJ U U UJ UJ UJ UJ U UJ UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U J U U U U U UJ U U U J J J U J U U U U U U U U U U J U U U J U U Validation Note F L M, F, B M, F, B M, F, B F, B M, B M, B M, F, B F F, B F, B M, F, B M, F, B M, F, B B F, B M, F, B M, F, B M, F, B M, F, B F, B M, F, B M, F, B M, F, B M, B M, F, B L L L Q Q F B Boeing Soil Char Level  (mg/kg) 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 0.5 1.29 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL No Yes No No SL No SL No No No No Yes No No No No No No No Ratio Boeing Soil Char Level 4.22E‐03 1.73E‐01 1.46E‐03 5.23E‐02 2.33E‐04 3.21E‐05 1.55E‐03 5.15E‐03 7.73E‐04 4.39E‐03 4.39E‐02 4.39E‐03 2.30E‐04 4.39E‐03 1.42E‐03 1.50E‐02 3.15E‐05 1.91E‐03 4.39E‐03 1.16E‐04 1.31E‐03 1.42E‐03 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.48E‐01 1.07E+00 No SL No SL No SL No SL 1.07E+00 No SL No SL No SL No SL 3.82E‐03 No SL No SL No SL 1.07E+00 No SL No SL 3.75E‐04 2.55E‐03 3.45E‐02 2.90E‐03 2.41E‐03 9.29E‐04 2.28E‐02 1.39E‐01 7.88E‐01 7.88E‐01 No SL No SL 1.74E‐02 1.20E‐03 No SL 2.09E‐04 No SL 8.60E‐02 1.04E+00 3.26E‐01 No SL No SL 1.50E‐01 1.00E‐01 2.20E‐01 4.19E‐01 1.06E+00 1.41E‐01 7.20E‐01 3.53E‐01 4.32E‐01 1.61E‐01 2.53E‐02 1.21E‐02 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background Ecological RBSL MRL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 19 19 19 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.1 1.1 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 1.04 1.04 5.22 5.22 5.22 5.22 10.4 10.4 5.22 5.22 1.04 1.04 320 320 630 320 630 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.8 1.8 38 18 94 13 18 25 2600 2600 2.1 5.2 1 4.4 1 5.2 5.2 4.2 0.52 0.42 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.88 0.88 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 6.2 6.2 6.2 0.69 0.69 0.69 0.69 0.35 0.35 0.69 0.69 0.69 0.69 0.69 0.35 0.69 0.69 0.69 0.69 0.69 0.69 0.69 0.21 0.21 0.00527 0.0199 0.0104 0.0096 0.0172 0.00886 0.0186 0.0119 0.0178 0.016 0.0287 0.00886 0.0158 0.0225 0.0297 0.00696 0.0199 0.0097 0.0178 0.0311 0.021 0.0159 0.0287 0.0225 0.0297 110 110 210 110 210 110 110 210 260 160 210 260 110 1600 1600 130 110 160 0.86 0.79 13 6.5 46 4.2 9.4 9.4 800 790 0.1 1 0.42 1.9 0.42 0.1 1.7 2.2 0.19 0.15 3.5 3.5 3.8 4.9 8.4 3.5 3.5 3.5 5.2 0.35 0.35 0.35 0.35 0.18 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2001 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2001S003 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/18/13 12:50 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Analysis  Method 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A Analyte beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Page 48 of 108 CAS Number 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 Result  Value 1.1 18 0.88 1.8 1.8 0.88 1.8 1.8 1.8 1.9 0.88 0.88 0.88 1.8 7.1 35 2 5.85 6.79 9.31 26.4 219 1.42 1.06 4.4 1.08 8.15 0.336 10.2 0.397 2.73 1.54 0.296 0.098 0.43 63.8 509 30.6 71.8 67.1 3210 7.47 11.9 3.85 2.52 310 310 620 310 620 310 310 310 310 310 310 410 310 2100 2100 310 310 310 1.8 1.8 37 18 93 12 18 25 2600 2600 0.1 9.9 1.3 4.2 0.41 0.43 2.8 0.19 18 18 18 18 18 18 18 18 18 1.8 0.6 1.5 0.86 0.86 1 18 0.86 1.8 1.8 0.86 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.0011 mg/kg 0.018 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0071 mg/kg 0.035 mg/kg 2 mg/kg 0.00000585 mg/kg 0.00000679 mg/kg 0.00000931 mg/kg 0.0000264 mg/kg 0.000219 mg/kg 0.00000142 mg/kg 0.00000106 mg/kg 0.0000044 mg/kg 0.00000108 mg/kg 0.00000815 mg/kg 0.000000336 mg/kg 0.0000102 mg/kg 0.000000397 mg/kg 0.00000273 mg/kg 0.00000154 mg/kg 0.00000516 mg/kg 0.000000098 mg/kg 0.00000043 mg/kg 0.00000516 mg/kg 0.000509 mg/kg 0.00000516 mg/kg 0.00000516 mg/kg 0.0000671 mg/kg 0.00321 mg/kg 0.00000516 mg/kg 0.00000516 mg/kg 0.00000103 mg/kg 0.00000103 mg/kg 0.31 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.41 mg/kg 0.31 mg/kg 2.1 mg/kg 2.1 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.037 mg/kg 0.018 mg/kg 0.093 mg/kg 0.012 mg/kg 0.018 mg/kg 0.025 mg/kg 2.6 mg/kg 2.6 mg/kg 2.1 mg/kg 9.9 mg/kg 1.3 mg/kg 4.2 mg/kg 1 mg/kg 0.43 mg/kg 5.2 mg/kg 0.52 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0006 mg/kg 0.0015 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.001 mg/kg 0.018 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00086 mg/kg Detected N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y N N N N N N N N N N N N Y Y N N N N N N N N Project  Qual  Code Validation Note U U U U U U U U U U U U U U U U U J J J J J J J J J UJ J J UJ UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U UJ U J J J U J U U U U U U U U U U U U J J U U U U U U U U F, F, B Q, Q, F, F, B F, F, B F, F, B F, F, B B, F, F F F, F, B F, F, B F, F, B F, B F, F, B M, F, F, B M, F, F, B F, F, B M, F, F, B M, F, F, B F, F, B Q, Q, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B L Q, Q, L Q, Q Q Q Q F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.31E‐02 Ecological RBSL 0.013 No 1.38E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 4.00E‐03 Ecological RBSL 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.17E‐02 Ecological RBSL 0.087 No 1.01E‐02 Ecological RBSL 0.0017 No 5.18E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.84E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 43 No 4.65E‐02 Ecological RBSL 0.0000057 Yes 1.03E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.65E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.37E‐01 Ecological RBSL 0.3 Yes 1.03E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL 0.3 Yes 1.03E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 3.73E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.03E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.75E‐04 Ecological RBSL 0.55 No 3.27E‐03 Ecological RBSL 1.1 No 3.36E‐02 Ecological RBSL 6.2 No 2.90E‐03 Ecological RBSL 39 No 2.38E‐03 Ecological RBSL 14 No 8.57E‐04 Ecological RBSL 0.79 No 2.28E‐02 Ecological RBSL 0.18 No 1.39E‐01 Ecological RBSL 3.3 No 7.88E‐01 MRL 3.3 No 7.88E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 3.71E‐02 Ecological RBSL 2340 No 1.79E‐03 Ecological RBSL ‐‐ No SL No SL 863.2 No 4.98E‐04 Background ‐‐ No SL No SL 0.5 Yes 1.04E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.50E‐01 Ecological RBSL 0.18 No 1.00E‐01 Ecological RBSL 0.082 No 2.20E‐01 Ecological RBSL 0.043 No 4.19E‐01 Ecological RBSL 0.017 Yes 1.06E+00 MRL 0.039 No 4.62E‐01 Ecological RBSL 0.025 No 7.20E‐01 Ecological RBSL 0.0051 No 3.53E‐01 Ecological RBSL 0.004164 No 1.44E‐01 Background 0.006101 No 2.46E‐01 Background 0.0348 No 2.47E‐02 Suburban Residential RBSL 0.073 No 1.18E‐02 Ecological RBSL 0.394 No 2.54E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.28E‐02 Ecological RBSL 0.013 No 1.38E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 3.91E‐03 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 1.1 18 0.88 1.8 1.8 0.88 1.8 1.8 1.8 1.9 0.88 0.88 0.88 1.8 7.1 35 2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.32 4.2 0.19 0.35 0.35 0.23 0.35 0.35 0.35 0.35 0.18 0.32 0.2 0.35 1.8 12 1.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 5.16 5.16 5.16 5.16 5.16 5.16 5.16 5.16 5.16 5.16 5.16 5.16 5.16 1.03 1.03 5.16 5.16 5.16 5.16 10.3 10.3 5.16 5.16 1.03 1.03 310 310 620 310 620 310 310 310 310 310 310 410 310 2100 2100 310 310 310 1.8 1.8 37 18 93 12 18 25 2600 2600 2.1 5.2 1 4.4 1 5.2 5.2 0.52 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.86 0.86 1 18 0.86 1.8 1.8 0.86 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0301 0.145 0.036 0.0402 0.0599 0.0378 0.0642 0.046 0.0612 0.0321 0.0863 0.0369 0.0307 0.0392 0.0509 0.0327 0.145 0.04 0.0617 0.0317 0.0755 0.0313 0.0863 0.0392 0.0509 100 100 360 100 360 100 100 210 260 160 210 260 100 1600 1600 130 100 160 0.85 0.78 12 6.4 46 4.1 9.3 9.3 790 780 0.1 1 0.41 1.8 0.41 0.1 1.7 0.19 3.4 3.4 3.7 4.8 8.3 3.4 3.4 3.4 5.1 0.34 0.34 0.34 0.34 0.18 0.31 8.4 0.19 0.34 0.34 0.23 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S001 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S002 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 8:40 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:50 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans VOCs Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 7199 8315A 1613B 1613B 1613B 8260B 1613B 8015B 8015B 8015B 8015B 8015B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal Xylenes, Total 2,3,7,8‐Tetrachlorodibenzofuran C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane Page 49 of 108 CAS Number 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 1330207 51207319 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 Result  Value 1.8 1.8 1.8 1.9 0.86 0.86 0.86 1.8 7 34 5.3 5.3 5.1 5.3 9.3 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 0.37 2 1.5 3.5 1.1 1.3 4.4 1.8 7.6 1.8 0.93 1.1 2.4 6.5 4.3 3.2 2.1 0.0157 0.0157 0.0597 5 0.0514 5.6 5.6 5.6 5.6 11 5 5 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 0.89 3.8 0.91 2 1.9 0.89 4.5 1.9 6.9 1.9 1.9 1.9 2.7 6.1 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg ug/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.007 mg/kg 0.034 mg/kg 5.3 mg/kg 5.3 mg/kg 5.1 mg/kg 5.3 mg/kg 9.3 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00037 mg/kg 0.002 mg/kg 0.0015 mg/kg 0.0035 mg/kg 0.0011 mg/kg 0.0013 mg/kg 0.0044 mg/kg 0.0018 mg/kg 0.0076 mg/kg 0.0018 mg/kg 0.00093 mg/kg 0.0011 mg/kg 0.0024 mg/kg 0.0065 mg/kg 0.0043 mg/kg 3.2 mg/kg 2.1 mg/kg 1.57E‐08 mg/kg 1.57E‐08 mg/kg 5.97E‐08 mg/kg 0.005 mg/kg 0.00000109 mg/kg 5.6 mg/kg 5.6 mg/kg 5.6 mg/kg 5.6 mg/kg 11 mg/kg 0.005 mg/kg 0.005 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00089 mg/kg 0.0038 mg/kg 0.00091 mg/kg 0.002 mg/kg 0.0019 mg/kg 0.00089 mg/kg 0.0045 mg/kg 0.0019 mg/kg 0.0069 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0027 mg/kg 0.0061 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg Detected N N N N N N N N N N N N Y N Y N N N N N N N N N N N Y Y Y Y Y Y Y N Y N Y Y Y Y N Y N Y Y Y N N N N N N N N N N N N N N N N N N N N Y Y Y Y N Y Y N Y N N N Y Y N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code U U U U U U U U U U U U J U J U U U U U U U U U U U J Validation Note F, F F F, F F J J J J U J U J J J J U Q Q, Q Q, Q Q, Q B U U U U U U U U U U U U U U U U U U U U U J J U J U U U U U U U U U U U U U U U U U U U U U U U U U F, F F F, F F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.15E‐02 Ecological RBSL 0.087 No 9.89E‐03 Ecological RBSL 0.0017 No 5.06E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.80E‐03 Ecological RBSL 0.493 No 6.90E‐02 Suburban Residential RBSL 1400 No 3.79E‐03 1400 No 3.79E‐03 1400 No 3.64E‐03 1 Yes 5.30E+00 1400 No 6.64E‐03 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 1.46E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 5.45E‐03 Ecological RBSL 2.2 No 1.68E‐04 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 0.0387 No 3.88E‐02 Suburban Residential RBSL 0.387 No 9.04E‐03 Suburban Residential RBSL 7.4 No 1.49E‐04 Ecological RBSL 0.387 No 3.36E‐03 Suburban Residential RBSL 1.2 No 3.67E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 1.41E‐04 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 2.40E‐03 Suburban Residential RBSL 14.6 No 7.53E‐05 Suburban Residential RBSL 1.3 No 1.85E‐03 Ecological RBSL 1.2 No 5.42E‐03 Ecological RBSL 0.5 No 8.60E‐03 Ecological RBSL 1.29 Yes 2.48E+00 Suburban Residential RBSL 43 No 4.88E‐02 Ecological RBSL 0.0000057 No 2.75E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 1.06E‐01 Background 3.4 No 1.47E‐03 Ecological RBSL ‐‐ No SL No SL 1400 No 4.00E‐03 1400 No 4.00E‐03 1400 No 4.00E‐03 1 Yes 5.60E+00 1400 No 7.86E‐03 10 No 5.00E‐04 Ecological RBSL 0.022 No 2.27E‐01 Ecological RBSL 0.32 No 6.25E‐02 Ecological RBSL 90 No 2.22E‐04 Ecological RBSL 2.3 No 8.70E‐03 Ecological RBSL 4.5 No 4.44E‐03 Ecological RBSL 0.11 No 1.82E‐01 Ecological RBSL 13 No 1.54E‐03 Ecological RBSL 0.0325 No 5.85E‐02 Suburban Residential RBSL 7.29 No 2.61E‐04 Suburban Residential RBSL 53 No 3.58E‐05 Ecological RBSL 1.1 No 1.73E‐03 Ecological RBSL 0.33 No 5.76E‐03 Ecological RBSL 2.2 No 4.05E‐04 Ecological RBSL 0.387 No 9.82E‐03 Suburban Residential RBSL 0.0387 No 2.35E‐02 Suburban Residential RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 7.4 No 2.57E‐04 Ecological RBSL 0.387 No 2.30E‐03 Suburban Residential RBSL 1.2 No 3.75E‐03 Ecological RBSL 0.113 No 1.68E‐02 Suburban Residential RBSL 54 No 1.28E‐04 Ecological RBSL 0.89 No 2.13E‐03 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 14.6 No 1.30E‐04 Suburban Residential RBSL 1.3 No 2.08E‐03 Ecological RBSL 1.2 No 5.08E‐03 Ecological RBSL 2.87 No 1.74E‐03 Suburban Residential RBSL 2460 No 2.03E‐06 Ecological RBSL 0.288 No 1.74E‐02 Suburban Residential RBSL 220 No 2.27E‐05 Ecological RBSL 0.533 No 9.38E‐03 Suburban Residential RBSL 1.89 No 2.65E‐03 Suburban Residential RBSL 6.9 No 7.25E‐04 Ecological RBSL ‐‐ No SL No SL 10 No 5.00E‐04 Ecological RBSL ‐‐ No SL No SL 3.1 No 1.61E‐03 Ecological RBSL 0.0978 No 5.11E‐02 Suburban Residential RBSL 0.104 No 4.81E‐02 Suburban Residential RBSL 130 No 3.85E‐05 Ecological RBSL 0.261 No 1.92E‐02 Suburban Residential RBSL 0.439 No 1.14E‐02 Suburban Residential RBSL 3.2 No 1.56E‐03 Ecological RBSL 23 No 2.17E‐04 Ecological RBSL ‐‐ No SL No SL 1.33 No 3.76E‐03 Suburban Residential RBSL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 1.8 1.8 1.8 1.9 0.86 0.86 0.86 1.8 7 34 5.3 5.3 5.3 5.3 11 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.3 0.43 2.1 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 0.34 0.34 0.34 0.34 0.18 0.31 0.2 0.34 1.8 11 2.1 2.1 2.1 2.1 4.3 6.4 6.4 6.4 6.4 6.4 6.4 0.71 0.71 0.71 0.71 0.35 0.35 0.71 0.71 0.71 0.71 0.71 0.35 0.71 0.71 0.71 0.71 0.71 0.71 0.71 2.2 0.15 1.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 5 1.09 5.6 5.6 5.6 5.6 11 5 5 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1 0.0514 2.2 2.2 2.2 2.2 4.5 1 2 6.7 6.7 6.7 6.7 6.7 6.7 0.74 0.74 0.74 0.74 0.37 0.37 0.74 0.74 0.74 0.74 0.74 0.37 0.74 0.74 0.74 0.74 0.74 0.74 0.74 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 ug/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 Analyte 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Page 50 of 108 CAS Number 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 Result  Value 10 10 10 19 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 49 5 5 5 5 5 5 5 5 5 0.691 3.79 0.0865 0.0892 0.116 0.0337 0.17 0.0917 0.231 0.0995 0.0828 0.0734 0.0816 0.0222 2.05 10.3 0.963 1.55 2.14 47.4 0.426 0.56 0.0448 0.157 340 340 670 340 670 340 340 340 340 340 340 450 340 2200 2200 340 340 340 1.9 1.9 40 19 100 13 19 27 2800 2800 0.27 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Result  in SL Units SL Units 0.01 mg/kg 0.01 mg/kg 0.01 mg/kg 0.019 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.01 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.049 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.000000691 mg/kg 0.00000379 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000109 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000214 mg/kg 0.0000474 mg/kg 0.00000545 mg/kg 0.00000545 mg/kg 0.00000109 mg/kg 0.00000109 mg/kg 0.34 mg/kg 0.34 mg/kg 0.67 mg/kg 0.34 mg/kg 0.67 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.45 mg/kg 0.34 mg/kg 2.2 mg/kg 2.2 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.04 mg/kg 0.019 mg/kg 0.1 mg/kg 0.013 mg/kg 0.019 mg/kg 0.027 mg/kg 2.8 mg/kg 2.8 mg/kg 0.27 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N N N N N N N N N N N N N N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J J UJ U UJ U UJ UJ U UJ UJ UJ UJ U UJ UJ UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U J Validation Note F, F, B F, F, B M, B, F, F F, F, B M, F, F, B F, F, B M, F M, F, F, B F, F, B M, F, F, B M, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B F, F, B F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B L L Boeing Soil Char Level  (mg/kg) 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 7.28 22.3 41 ‐‐ 2.31 1.3 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 ‐‐ ‐‐ ‐‐ 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ Exceeds Boeing Soil Char Level No No No No No No No SL No No No No No No SL No No No SL No No SL No No No No SL No No No No SL No No No No No No No No No No SL No No SL No SL No SL No No No No No SL No No No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL Ratio Boeing Soil Char Level 1.00E+00 4.35E‐04 2.22E‐03 4.13E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 6.87E‐04 2.24E‐04 1.22E‐04 No SL 2.16E‐03 3.85E‐03 1.23E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 No SL No SL No SL 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.70E‐01 1.13E+00 No SL No SL No SL No SL 1.13E+00 No SL No SL No SL No SL 4.09E‐03 No SL No SL No SL 1.13E+00 No SL No SL 3.96E‐04 3.45E‐03 3.64E‐02 3.06E‐03 2.56E‐03 9.29E‐04 2.41E‐02 1.50E‐01 8.48E‐01 8.48E‐01 No SL SCL Basis MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 10 10 10 19 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 49 5 5 5 5 5 5 5 5 5 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 5.45 1.09 5.45 5.45 5.45 5.45 10.9 10.9 5.45 5.45 1.09 1.09 340 340 670 340 670 340 340 340 340 340 340 450 340 2200 2200 340 340 340 1.9 1.9 40 19 100 13 19 27 2800 2800 2.2 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 2 3 3 7 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 2 1 1 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 19 1 1 1 1 1 1 1 2 1 0.016 0.0393 0.0205 0.0181 0.0288 0.0174 0.0309 0.0186 0.0282 0.0172 0.027 0.0174 0.0158 0.0222 0.018 0.0393 0.0178 0.0292 0.0264 0.0308 0.0165 0.027 0.0214 0.0222 110 110 220 110 220 110 110 220 280 170 220 280 110 1700 1700 140 110 170 0.92 0.84 13 6.9 49 4.5 10 10 850 840 0.11 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2002 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2002S003 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S001 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/12/13 9:00 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 10:55 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH Analysis  Method 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7199 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Hexavalent Chromium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Page 51 of 108 CAS Number 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 18540299 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 Result  Value 69.5 11.2 6.2 0.45 0.26 54.1 4.5 0.2 22100 105 0.811 3.53 26.1 5.08 33.2 229 1530 722 41 44.6 4.26 0.189 8.45 0.0708 9.67 5.87 0.302 17 0.11 0.145 0.229 0.22 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.93 0.93 1.1 19 0.93 1.9 1.9 0.93 1.9 1.9 1.9 2 0.93 0.93 0.93 1.9 7.5 37 2.2 33200 182 1.14 7.83 32.9 8.4 33.6 493 2320 156 58.9 58.6 5.74 0.331 7.8 0.264 14.9 11.4 0.572 24.7 0.207 0.0997 0.405 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 69.5 11.2 6.2 1.1 0.26 54.1 0.0045 0.56 22100 105 0.811 3.53 26.1 5.08 33.2 229 1530 722 41 44.6 4.26 0.22 8.45 0.0708 9.67 5.87 0.302 17 0.439 0.145 0.229 0.22 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.0019 0.0019 0.0019 0.00093 0.00093 0.0011 0.019 0.00093 0.0019 0.0019 0.00093 0.0019 0.0019 0.0019 0.002 0.00093 0.00093 0.00093 0.0019 0.0075 0.037 2.2 33200 182 1.14 7.83 32.9 8.4 33.6 493 2320 156 58.9 58.6 5.74 0.331 7.8 0.264 14.9 11.4 0.572 24.7 0.207 0.0997 0.405 5.5 5.5 5.5 5.5 11 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.0018 0.0018 0.0018 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y N Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N Project  Qual  Code J J U J U U Validation Note Q Q Q F, B B J F J U B J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U B B J J U U U U U U U U U U U U U U U F F F Boeing Soil Char Level  (mg/kg) ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 1.29 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 0.075 0.087 0.0017 0.0328 2.5 0.493 43 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 Exceeds Boeing Soil Char Level No SL No No No SL No No SL No Yes No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No No Ratio Boeing Soil Char Level No SL 3.20E‐01 2.65E‐03 No SL 3.01E‐04 No SL 9.00E‐03 1.12E+00 5.83E‐01 5.15E‐01 1.69E‐01 1.60E‐01 4.34E‐01 1.94E‐01 5.16E‐01 3.17E‐01 2.03E‐01 9.58E‐01 3.67E‐01 2.92E‐01 4.00E‐01 4.40E‐01 3.49E‐01 1.63E‐01 2.30E‐01 1.73E‐01 1.84E‐01 2.65E‐01 4.39E‐01 1.46E‐01 3.01E‐01 1.71E‐01 No SL No SL 1.58E‐01 1.06E‐01 2.32E‐01 4.42E‐01 1.12E+00 4.87E‐01 7.60E‐01 3.73E‐01 4.56E‐01 3.11E‐01 2.67E‐02 1.27E‐02 2.79E‐03 1.73E‐02 1.39E‐02 1.46E‐01 8.26E‐03 4.23E‐03 8.64E‐03 2.41E‐01 2.07E‐01 2.33E‐01 1.24E‐02 1.07E‐02 5.47E‐01 5.79E‐02 3.00E‐03 7.51E‐02 5.12E‐02 8.76E‐01 8.93E‐01 2.38E‐01 3.56E‐01 5.47E‐01 3.21E‐01 5.22E‐01 6.82E‐01 3.08E‐01 2.07E‐01 5.27E‐01 3.83E‐01 5.39E‐01 6.62E‐01 3.22E‐01 6.07E‐01 3.55E‐01 3.36E‐01 3.48E‐01 3.85E‐01 2.07E‐01 1.01E‐01 5.32E‐01 3.93E‐03 3.93E‐03 3.93E‐03 5.50E+00 7.86E‐03 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 SCL Basis Ecological RBSL Ecological RBSL Background Ecological RBSL MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 28 1.1 4.9 1.1 5.6 5.6 4.5 0.56 11 0.549 0.274 5.49 0.823 0.549 2.2 0.549 54.9 54.9 0.549 2.2 5.49 0.22 0.439 0.11 0.22 0.22 0.11 0.439 0.439 0.11 0.11 0.45 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.93 0.93 1.1 19 0.93 1.9 1.9 0.93 1.9 1.9 1.9 2 0.93 0.93 0.93 1.9 7.5 37 2.2 11.1 0.554 0.277 5.54 0.831 0.554 2.2 0.554 55.4 55.4 0.554 2.22 5.54 0.222 0.443 0.111 0.222 0.222 0.111 0.443 0.443 0.111 0.111 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.6 0.45 2 0.45 0.11 1.8 2.4 0.2 8.46 0.0362 0.0736 0.911 0.0966 0.0988 0.6 0.0911 14.8 18.3 0.121 0.22 0.911 0.0747 0.0922 0.0505 0.16 0.016 0.0571 0.169 0.11 0.022 0.0329 0.16 3.7 3.7 4 5.1 8.9 3.7 3.7 3.7 5.5 0.37 0.37 0.37 0.37 0.19 0.34 4.5 0.2 0.37 0.37 0.25 0.37 0.37 0.37 0.37 0.19 0.34 0.21 0.37 1.9 12 1.3 8.55 0.0366 0.0743 0.92 0.0976 0.0998 0.61 0.092 15 18.5 0.122 0.222 0.92 0.0754 0.0931 0.051 0.162 0.0162 0.0554 0.171 0.111 0.0222 0.0333 2.2 2.2 2.2 2.2 4.4 6.6 6.6 6.6 6.6 6.6 6.6 0.73 0.73 0.73 0.73 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S002 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:00 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8015B 8015B 8015B 8015B 8015B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene Page 52 of 108 CAS Number 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 Result  Value 1.8 1.8 0.73 1.8 0.81 1.8 1.8 0.79 1.8 0.96 1.8 1.8 1.8 1.8 1.8 5 5.8 5.8 5.8 5.8 12 5 5 21 21 21 21 21 21 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 0.61 1.9 0.96 1.9 1.9 1.9 1.9 1.9 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 21 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0018 0.0018 0.00073 0.0018 0.00081 0.0018 0.0018 0.00079 0.0018 0.00096 0.0018 0.0018 0.0018 0.0018 0.0018 0.005 5.8 5.8 5.8 5.8 12 0.005 0.005 0.021 0.021 0.021 0.021 0.021 0.021 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.00061 0.0019 0.00096 0.0019 0.0019 0.0019 0.0019 0.0019 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.01 0.01 0.021 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N Y N Y N N Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U J U J U U J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note F, Original Result = 1 F F F F Boeing Soil Char Level  (mg/kg) 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 3.4 1400 1400 1400 1 1400 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 7.28 22.3 41 ‐‐ 2.31 1.3 8160 ‐‐ 2.97 3.3 61 73 16 3.4 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No SL No No No No No No SL No No No SL No No SL No No No No SL No No No No SL No No No No No No Ratio Boeing Soil Char Level 5.45E‐03 8.18E‐04 1.89E‐03 4.65E‐02 2.09E‐03 2.43E‐04 4.65E‐03 6.58E‐04 1.59E‐02 1.78E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 1.47E‐03 4.14E‐03 4.14E‐03 4.14E‐03 5.80E+00 8.57E‐03 5.00E‐04 2.27E‐01 6.56E‐02 2.33E‐04 9.13E‐03 4.67E‐03 1.91E‐01 1.62E‐03 5.85E‐02 2.61E‐04 3.58E‐05 1.73E‐03 5.76E‐03 8.64E‐04 4.91E‐03 4.91E‐02 4.91E‐03 2.57E‐04 4.91E‐03 5.08E‐04 1.68E‐02 1.78E‐05 2.13E‐03 4.91E‐03 1.30E‐04 1.46E‐03 1.58E‐03 1.74E‐03 2.03E‐06 1.74E‐02 2.27E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 1.00E+00 4.35E‐04 2.22E‐03 4.57E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 6.87E‐04 2.24E‐04 1.22E‐04 No SL 2.16E‐03 3.85E‐03 1.23E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5 5.8 5.8 5.8 5.8 12 5 5 21 21 21 21 21 21 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 21 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 0.37 0.37 0.73 0.73 0.73 0.73 0.73 0.37 0.73 0.73 0.73 0.73 0.73 0.73 0.73 1 2.3 2.3 2.3 2.3 4.7 1 2 7 7 7 7 7 7 0.78 0.78 0.78 0.78 0.39 0.39 0.78 0.78 0.78 0.78 0.78 0.39 0.78 0.78 0.78 0.78 0.78 0.78 0.78 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 7 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 2 1 1 1 4 0.5 2 1 1 1 1 1 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2003 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2003S003 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S001 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 ELBS2004S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 11:10 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:20 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 6/17/13 12:35 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Page 53 of 108 CAS Number 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 Result  Value 5 5 5 5 5 5 52 5 5 5 5 5 5 5 5 5 15500 115 0.513 4.84 31.7 7.64 32.4 408 2110 135 49.7 58.6 3.94 0.15 9.47 0.193 17.1 6.31 0.33 31 0.113 0.0439 0.34 15600 111 0.616 5.76 19.4 6.06 15.6 371 3320 92.8 34.9 43.8 3.48 0.198 4.68 0.261 15.1 7.65 0.621 16.8 0.144 0.0297 0.281 19 19 19 19 19 19 19 4.7 19 5.6 5.6 3.9 5.6 12 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 0.81 1.9 1.9 0.8 1.9 0.98 1.9 1.9 2.2 0.98 1.9 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.005 0.005 0.005 0.005 0.005 0.005 0.052 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 15500 115 0.513 5.67 31.7 7.64 32.4 408 2110 135 49.7 58.6 3.94 0.227 9.47 0.193 17.1 6.31 0.33 31 0.454 0.0439 0.34 15600 111 0.616 5.42 19.4 6.06 15.6 371 3320 92.8 34.9 43.8 3.48 0.198 4.68 0.261 15.1 7.65 0.621 16.8 0.144 0.0297 0.281 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.0047 0.019 5.6 5.6 3.9 5.6 12 0.02 0.02 0.02 0.02 0.02 0.02 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.0019 0.00081 0.0019 0.0019 0.0008 0.0019 0.00098 0.0019 0.0019 0.0022 0.00098 0.0019 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N N N Y N Y N N N N N N N N N N N N N N Y N N Y N Y N N Y Y N Project  Qual  Code Validation Note U U U U U U U U U U U U U U U U B U B J U B U J B U B J J J J U U U U U U U J U U U J U U U U U U U U U U U U U U U J U U J U J U U J U F F F F, Original Result = 0.98 Boeing Soil Char Level  (mg/kg) 16 3.7 0.98 ‐‐ 210 ‐‐ ‐‐ ‐‐ 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 Exceeds Boeing Soil Char Level No No No No SL No No SL No SL No SL No No No No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 No SL No SL No SL 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 4.09E‐01 5.64E‐01 1.07E‐01 2.58E‐01 5.27E‐01 2.92E‐01 5.03E‐01 5.64E‐01 2.80E‐01 1.79E‐01 4.45E‐01 3.83E‐01 3.70E‐01 4.54E‐01 3.91E‐01 4.44E‐01 4.07E‐01 1.86E‐01 2.01E‐01 4.83E‐01 4.54E‐01 4.43E‐02 4.47E‐01 4.12E‐01 5.45E‐01 1.28E‐01 2.46E‐01 3.23E‐01 2.31E‐01 2.42E‐01 5.13E‐01 4.41E‐01 1.23E‐01 3.12E‐01 2.86E‐01 3.27E‐01 3.96E‐01 1.93E‐01 6.00E‐01 3.60E‐01 2.26E‐01 3.78E‐01 2.62E‐01 1.44E‐01 3.00E‐02 3.69E‐01 No SL No SL 1.58E‐01 1.06E‐01 2.32E‐01 4.42E‐01 1.12E+00 1.21E‐01 7.60E‐01 4.00E‐03 4.00E‐03 2.79E‐03 5.60E+00 8.57E‐03 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.85E‐02 2.61E‐04 3.58E‐05 1.73E‐03 5.76E‐03 8.64E‐04 4.91E‐03 4.91E‐02 2.09E‐03 2.57E‐04 4.91E‐03 6.67E‐04 1.68E‐02 1.81E‐05 2.13E‐03 4.91E‐03 1.51E‐04 7.54E‐04 1.58E‐03 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5 5 5 5 5 5 52 5 5 5 5 5 5 5 5 5 11.3 0.567 0.284 5.67 0.851 0.567 2.3 0.567 56.7 56.7 0.567 2.27 5.67 0.227 0.454 0.113 0.227 0.227 0.113 0.454 0.454 0.113 0.113 10.8 0.542 0.271 5.42 0.814 0.542 2.2 0.542 54.2 54.2 0.542 2.17 5.42 0.217 0.434 0.108 0.217 0.217 0.108 0.434 0.434 0.108 0.108 19 19 19 19 19 19 19 19 19 5.6 5.6 5.6 5.6 11 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1 1 1 1 1 1 21 1 1 1 1 1 1 1 2 1 8.74 0.0374 0.076 0.941 0.0998 0.102 0.62 0.0941 15.3 18.9 0.125 0.227 0.941 0.0771 0.0953 0.0522 0.166 0.0166 0.0567 0.175 0.113 0.0227 0.034 8.36 0.0358 0.0727 0.9 0.0955 0.0976 0.6 0.09 14.6 18.1 0.119 0.217 0.9 0.0738 0.0911 0.0499 0.158 0.0158 0.0542 0.167 0.108 0.0217 0.0325 3.7 3.7 4 5.1 8.9 3.7 3.7 3.7 5.4 2.2 2.2 2.2 2.2 4.4 6.7 6.7 6.7 6.7 6.7 6.7 0.74 0.74 0.74 0.74 0.37 0.37 0.74 0.74 0.74 0.74 0.74 0.37 0.74 0.74 0.74 0.74 0.74 0.74 0.74 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2004 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2004S003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 12:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Analysis  Method 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8015B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 300.0 300.0 300.0 300.0 300.0 300.0 Analyte C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol Bromide Chloride Fluoride Nitrate‐NO3 Ortho Phosphate (as PO4) Sulfate Page 54 of 108 CAS Number EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 24959679 16887006 16984488 NO3 14265442 14808798 Result  Value 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.1 0.78 0.93 1.8 1.8 1.2 1.8 2.1 1.8 1.8 1.8 1.2 2.2 24500 118 0.844 6.77 28.5 5.86 32.8 289 2000 117 49.4 53.3 5.51 0.215 11.1 0.123 14.8 8.91 0.29 26.3 0.107 0.106 0.427 18 18 18 18 18 18 18 4.9 18 6.3 6.3 6.3 6.3 13 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.6 2 1 1.1 2.2 2.1 3.3 2.1 0.93 2.1 2 3.2 1.3 1.3 0.13 1.3 1.2 3.4 0.13 4.2 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 5.5 5.5 5.5 5.5 11 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0011 0.00078 0.00093 0.0018 0.0018 0.0012 0.0018 0.0021 0.0018 0.0018 0.0018 0.0012 0.0018 24500 118 0.844 6.77 28.5 5.86 32.8 289 2000 117 49.4 53.3 5.51 0.215 11.1 0.123 14.8 8.91 0.29 26.3 0.428 0.106 0.427 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.0049 0.018 6.3 6.3 6.3 6.3 13 1.3 0.023 0.023 0.023 0.023 0.023 0.023 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0016 0.002 0.001 0.0011 0.0022 0.0021 0.0033 0.0021 0.00093 0.0021 0.002 0.0021 1.3 1.3 2.5 6.3 1.2 3.4 6.3 6.3 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N Y Y Y N N Y N Y N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N N N N N Y N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y N Y N Y N Y N N N N N Y Y N N Project  Qual  Code U U U U U U U U U U U U U U U U U J J J U U J U U U U J U Validation Note F F F F B B U J U U U U U U U J U U U U U U U U U U U U U U U U U U U J J J J J F F F U U J U J U U U U U J J UJ U F Q Q F Boeing Soil Char Level  (mg/kg) 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 1400 1400 1400 1 1400 ‐‐ 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ 35 2340 863.2 ‐‐ Exceeds Boeing Soil Char Level No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No Yes No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No No No No SL Ratio Boeing Soil Char Level 3.93E‐03 3.93E‐03 3.93E‐03 5.50E+00 7.86E‐03 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 2.84E‐03 2.02E‐02 2.40E‐03 2.43E‐04 4.65E‐03 1.00E‐03 1.59E‐02 3.89E‐05 2.02E‐03 4.65E‐03 1.23E‐04 9.23E‐04 1.50E‐03 6.46E‐01 5.79E‐01 1.76E‐01 3.08E‐01 4.74E‐01 2.24E‐01 5.09E‐01 4.00E‐01 2.66E‐01 1.55E‐01 4.42E‐01 3.48E‐01 5.18E‐01 4.30E‐01 4.59E‐01 2.83E‐01 3.52E‐01 2.63E‐01 1.77E‐01 4.10E‐01 4.28E‐01 1.07E‐01 5.61E‐01 No SL No SL 1.50E‐01 1.00E‐01 2.20E‐01 4.19E‐01 1.06E+00 1.26E‐01 7.20E‐01 4.50E‐03 4.50E‐03 4.50E‐03 6.30E+00 9.29E‐03 No SL 7.19E‐02 2.56E‐04 1.00E‐02 5.11E‐03 2.09E‐01 1.77E‐03 6.46E‐02 2.88E‐04 3.96E‐05 1.91E‐03 6.36E‐03 9.55E‐04 5.43E‐03 4.13E‐02 5.17E‐03 1.35E‐04 2.84E‐03 1.83E‐03 1.86E‐02 6.11E‐05 2.36E‐03 2.40E‐03 1.44E‐04 1.54E‐03 1.75E‐03 No SL No SL No SL No SL 3.43E‐02 1.45E‐03 7.30E‐03 No SL SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 10.7 0.535 0.268 5.35 0.803 0.535 2.1 0.535 53.5 53.5 0.535 2.14 5.35 0.214 0.428 0.107 0.214 0.214 0.107 0.428 0.428 0.107 0.107 18 18 18 18 18 18 18 18 18 6.3 6.3 6.3 6.3 13 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.3 1.3 2.5 6.3 1.3 5.8 6.3 6.3 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 2.2 2.2 2.2 2.2 4.4 6.6 6.6 6.6 6.6 6.6 6.6 0.73 0.73 0.73 0.73 0.36 0.36 0.73 0.73 0.73 0.73 0.73 0.36 0.73 0.73 0.73 0.73 0.73 0.73 0.73 8.25 0.0353 0.0717 0.888 0.0942 0.0963 0.59 0.0888 14.4 17.9 0.118 0.214 0.888 0.0728 0.0899 0.0492 0.156 0.0156 0.0535 0.165 0.107 0.0214 0.0321 3.6 3.6 3.9 5 8.7 3.6 3.6 3.6 5.3 2.5 2.5 2.5 2.5 5 0.25 7.5 7.5 7.5 7.5 7.5 7.5 0.84 0.84 0.84 0.84 0.42 0.42 0.84 0.84 0.84 0.84 0.84 0.42 0.84 0.84 0.84 0.84 0.84 0.84 0.84 0.25 0.25 0.13 1.3 0.5 2.2 0.13 2 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y N Y N Y N N N N N N N Y Y N Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005D003 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S001 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:50 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:00 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Analysis  Method 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8315A 300.0 300.0 300.0 300.0 300.0 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8015B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Formaldehyde Bromide Chloride Fluoride Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Page 55 of 108 CAS Number 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 50000 24959679 16887006 16984488 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 Result  Value 22900 110 0.855 6.4 29.8 6.06 32.8 262 1590 155 47.2 57.2 5.21 0.15 13.2 0.167 15.4 8.99 0.223 23.7 0.123 0.12 0.346 21 21 21 21 21 21 21 8.1 21 2.5 0.11 5.3 1.8 0.64 40.3 13800 118 0.468 5.37 16.5 6.86 15.4 360 3780 218 41.2 48.8 3.81 0.181 5.75 0.242 15.9 10.3 0.53 14.1 0.17 0.0568 0.341 19 19 19 19 19 19 92 47 19 6.3 6.3 6.3 6.3 13 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 22900 110 0.855 6.4 29.8 6.06 32.8 262 1590 155 47.2 57.2 5.21 0.247 13.2 0.167 15.4 8.99 0.223 23.7 0.493 0.12 0.346 0.021 0.021 0.021 0.021 0.021 0.021 0.021 0.0081 0.021 2.5 2.2 5.3 1.8 0.64 40.3 13800 118 0.468 5.48 16.5 6.86 15.4 360 3780 218 41.2 48.8 3.81 0.181 5.75 0.242 15.9 10.3 0.53 14.1 0.17 0.0568 0.341 0.019 0.019 0.019 0.019 0.019 0.019 0.092 0.047 0.019 6.3 6.3 6.3 6.3 13 1.3 0.023 0.023 0.023 0.023 0.023 0.023 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y N N N N N N N Y N N N Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note B B J U B U J U U U U U U U J U U U J J J U Q Q F B B J J J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U F F F F Boeing Soil Char Level  (mg/kg) 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 43 ‐‐ ‐‐ 35 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 1400 1400 1400 1 1400 ‐‐ 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No SL No SL No No No SL No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes Yes No No No No Yes No No SL No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 6.04E‐01 5.40E‐01 1.78E‐01 2.91E‐01 4.96E‐01 2.31E‐01 5.09E‐01 3.62E‐01 2.11E‐01 2.06E‐01 4.22E‐01 3.74E‐01 4.90E‐01 4.94E‐01 5.45E‐01 3.84E‐01 3.67E‐01 2.65E‐01 1.36E‐01 3.69E‐01 4.93E‐01 1.21E‐01 4.55E‐01 No SL No SL 1.75E‐01 1.17E‐01 2.56E‐01 4.88E‐01 1.24E+00 2.08E‐01 8.40E‐01 5.81E‐02 No SL No SL 5.14E‐02 7.41E‐04 No SL 3.64E‐01 5.79E‐01 9.75E‐02 2.49E‐01 2.74E‐01 2.62E‐01 2.39E‐01 4.98E‐01 5.02E‐01 2.89E‐01 3.69E‐01 3.19E‐01 3.58E‐01 3.62E‐01 2.38E‐01 5.56E‐01 3.79E‐01 3.04E‐01 3.23E‐01 2.20E‐01 1.70E‐01 5.74E‐02 4.48E‐01 No SL No SL 1.58E‐01 1.06E‐01 2.32E‐01 4.42E‐01 5.41E+00 1.21E+00 7.60E‐01 4.50E‐03 4.50E‐03 4.50E‐03 6.30E+00 9.29E‐03 No SL 7.19E‐02 2.56E‐04 1.00E‐02 5.11E‐03 2.09E‐01 1.77E‐03 6.46E‐02 2.88E‐04 3.96E‐05 1.91E‐03 6.36E‐03 9.55E‐04 5.43E‐03 5.43E‐02 5.43E‐03 2.84E‐04 5.43E‐03 1.75E‐03 1.86E‐02 3.89E‐05 2.36E‐03 5.43E‐03 1.44E‐04 1.62E‐03 1.75E‐03 SCL Basis Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 12.3 0.617 0.308 6.17 0.925 0.617 2.5 0.617 61.7 61.7 0.617 2.47 6.17 0.247 0.493 0.123 0.247 0.247 0.123 0.493 0.493 0.123 0.123 21 21 21 21 21 21 21 21 21 2.5 2.2 5.5 1.1 5.5 5.5 11 0.548 0.274 5.48 0.822 0.548 2.2 0.548 54.8 54.8 0.548 2.19 5.48 0.219 0.439 0.11 0.219 0.219 0.11 0.439 0.439 0.11 0.11 19 19 19 19 19 19 92 19 19 6.3 6.3 6.3 6.3 13 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 9.51 0.0407 0.0826 1.02 0.109 0.111 0.68 0.102 16.6 20.6 0.136 0.247 1.02 0.0839 0.104 0.0567 0.18 0.018 0.0617 0.19 0.123 0.0247 0.037 4.1 4.1 4.5 5.7 10 4.1 4.1 4.1 6.1 1.5 0.11 1.1 0.44 0.11 1.8 8.45 0.0362 0.0735 0.91 0.0965 0.0987 0.6 0.091 14.8 18.3 0.121 0.219 0.91 0.0746 0.0921 0.0504 0.16 0.016 0.0548 0.169 0.11 0.0219 0.0329 3.6 3.6 4 5.1 8.8 3.6 92 3.6 5.4 2.5 2.5 2.5 2.5 5 0.25 7.5 7.5 7.5 7.5 7.5 7.5 0.83 0.83 0.83 0.83 0.42 0.42 0.83 0.83 0.83 0.83 0.83 0.42 0.83 0.83 0.83 0.83 0.83 0.83 0.83 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N Y Y Y Y Y Y N Y Y Y N Y N Y Y N N N N N N N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S002SP ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 ELBS2005S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/17/13 9:15 6/17/13 9:15 6/17/13 9:15 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs Analysis  Method 8015B 8015B 8315A 8015B 8015B 8015B 8015B 8015B 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 8315A 8015B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 300.0 300.0 300.0 300.0 300.0 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 Analyte Ethanol Methanol Formaldehyde C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol Formaldehyde C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol Bromide Chloride Fluoride Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Page 56 of 108 CAS Number 64175 67561 50000 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 50000 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 24959679 16887006 16984488 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 Result  Value 1.3 1.3 2.4 2.17 2.17 2.17 2.17 5.14 216 216 216 216 216 216 216 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 37.9 5.14 2.4 5.5 5.5 5.5 5.5 11 1.1 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 0.46 1.5 1.1 1.4 1.9 0.86 1.6 1.9 2.4 1.9 1.9 1.9 2 2.5 1.1 1.1 0.11 1.9 0.87 0.11 8.4 17400 90.1 0.698 5.63 21.6 7.63 25.4 377 1380 124 40.5 41 4.25 0.16 13.8 0.132 11.7 8.77 0.229 20.4 0.109 0.0852 0.313 19 19 19 19 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 1.3 1.3 2.4 2.17 2.17 2.17 2.17 5.14 0.216 0.216 0.216 0.216 0.216 0.216 0.216 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 0.00432 37.9 5.14 2.4 5.5 5.5 5.5 5.5 11 1.1 0.02 0.02 0.02 0.02 0.02 0.02 0.0019 0.0019 0.0019 0.0019 0.0019 0.00046 0.0015 0.0011 0.0014 0.0019 0.00086 0.0016 0.0019 0.0024 0.0019 0.0019 0.0019 0.002 0.0019 1.1 1.1 2.2 1.9 0.87 5.5 5.5 17400 90.1 0.698 5.46 21.6 7.63 25.4 377 1380 124 40.5 41 4.25 0.218 13.8 0.132 11.7 8.77 0.229 20.4 0.437 0.0852 0.313 0.019 0.019 0.019 0.019 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y N Y Y N Y N N N Y N N N N Y Y N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y N N N N Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U U U U U U U U U U U U U J J J J U J J U Validation Note F F H F F F U U U U U U U J J UJ U U J U U J U U U U F Q F B B B Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ 43 1400 1400 1400 1 ‐‐ 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ 43 1400 1400 1400 1 1400 ‐‐ 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ 35 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 Exceeds Boeing Soil Char Level No SL No SL No No No No Yes No SL No No No No Yes No Yes No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No No No SL No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No Ratio Boeing Soil Char Level No SL No SL 5.58E‐02 1.55E‐03 1.55E‐03 1.55E‐03 2.17E+00 No SL 6.75E‐01 2.40E‐03 9.39E‐02 4.80E‐02 1.96E+00 1.66E‐02 6.65E+00 5.93E‐04 8.15E‐05 3.93E‐03 1.31E‐02 1.96E‐03 1.12E‐02 1.12E‐01 1.12E‐02 5.84E‐04 1.12E‐02 3.60E‐03 3.82E‐02 8.00E‐05 4.85E‐03 1.12E‐02 2.96E‐04 3.32E‐03 3.60E‐03 No SL No SL 5.58E‐02 3.93E‐03 3.93E‐03 3.93E‐03 5.50E+00 7.86E‐03 No SL 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.85E‐02 2.61E‐04 3.58E‐05 1.73E‐03 5.76E‐03 2.09E‐04 3.88E‐03 2.84E‐02 3.62E‐03 2.57E‐04 2.22E‐03 1.33E‐03 1.68E‐02 4.44E‐05 2.13E‐03 4.91E‐03 1.30E‐04 1.54E‐03 1.58E‐03 No SL No SL No SL No SL 2.49E‐02 6.37E‐03 No SL 4.59E‐01 4.42E‐01 1.45E‐01 2.48E‐01 3.59E‐01 2.91E‐01 3.94E‐01 5.21E‐01 1.83E‐01 1.64E‐01 3.62E‐01 2.68E‐01 3.99E‐01 4.36E‐01 5.70E‐01 3.03E‐01 2.79E‐01 2.59E‐01 1.39E‐01 3.18E‐01 4.37E‐01 8.61E‐02 4.11E‐01 No SL No SL 1.58E‐01 1.06E‐01 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.3 1.3 2.4 2.17 2.17 2.17 2.17 5.14 216 216 216 216 216 216 216 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 4.32 37.9 5.14 2.4 5.5 5.5 5.5 5.5 11 1.1 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.1 1.1 2.2 5.5 1.1 5.5 5.5 10.9 0.546 0.273 5.46 0.819 0.546 2.2 0.546 54.6 54.6 0.546 2.18 5.46 0.218 0.437 0.109 0.218 0.218 0.109 0.437 0.437 0.109 0.109 19 19 19 19 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg MDL MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA 0.25 0.25 1.5 0.716 0.716 0.716 0.716 1.29 64.9 64.9 64.9 64.9 64.9 64.9 64.9 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 1.08 0.648 1.08 1.08 11.4 1.29 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y 2.2 2.2 2.2 2.2 4.4 0.22 6.7 6.7 6.7 6.7 6.7 6.7 0.74 0.74 0.74 0.74 0.37 0.37 0.74 0.74 0.74 0.74 0.74 0.37 0.74 0.74 0.74 0.74 0.74 0.74 0.74 0.22 0.22 0.11 1.1 0.44 0.11 1.8 8.42 0.036 0.0731 0.906 0.0961 0.0983 0.6 0.0906 14.7 18.2 0.12 0.218 0.906 0.0742 0.0917 0.0502 0.159 0.0159 0.0546 0.168 0.109 0.0218 0.0328 3.7 3.7 4 5.1 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N Y N Y N Y Y Y Y Y Y Y N Y N N N N N N Y N Y N N N N N N Y N N N Y N Y N N Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2005S003 ELBS2006S001 ELBS2006S001 ELBS2006S001 ELBS2006S001 ELBS2006S001 ELBS2006S001 ELBS2006S001 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S002 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/17/13 9:35 6/13/13 9:00 6/13/13 9:00 6/13/13 9:00 6/13/13 9:00 6/13/13 9:00 6/13/13 9:00 6/13/13 9:00 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:05 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PCBs PCBs PCBs PCBs PCBs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8082 8082 8082 8082 8082 8315A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 8315A 8015B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 Analyte Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Formaldehyde Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol Formaldehyde C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Isopropanol bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Ethanol Methanol Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Page 57 of 108 CAS Number 11141165 53469219 12672296 11097691 11096825 50000 24959679 16887006 16984488 NO3 NO2 14265442 14808798 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 50000 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 67630 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 64175 67561 24959679 16887006 16984488 NO3 NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 Result  Value 19 19 19 19 19 2.1 0.12 3.7 0.94 2.9 0.48 0.3 16.2 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.3 1.3 2.6 6.3 6.3 6.3 6.3 13 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.2 2.1 2.1 1.3 1.3 0.32 98.3 1 2.2 0.5 0.13 82 24800 163 0.985 5.18 35.6 8.75 53.9 354 2890 252 52.5 75.7 1.78 0.085 26.2 0.165 14.5 7.75 0.375 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 0.019 0.019 0.019 0.019 0.019 2.1 2.4 3.7 0.94 2.9 1.2 0.3 16.2 1.3 0.023 0.023 0.023 0.023 0.023 0.023 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 1.3 1.3 2.6 6.3 6.3 6.3 6.3 13 1.3 0.023 0.023 0.023 0.023 0.023 0.023 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0012 0.0021 0.0021 1.3 1.3 0.32 98.3 1 5.8 1.3 6.3 82 24800 163 0.985 5.18 35.6 8.75 53.9 354 2890 252 52.5 75.7 1.78 0.25 26.2 0.165 14.5 7.75 0.375 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N Y Y Y N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N Y Y Y N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Project  Qual  Code U U U U U U U J J J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U J J U U UJ Validation Note Q Q Q F F F F F Q Q Q F J B, F B B J U B B Boeing Soil Char Level  (mg/kg) 0.082 0.043 0.017 0.039 0.025 43 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ ‐‐ 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ 43 1400 1400 1400 1 1400 ‐‐ 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 Exceeds Boeing Soil Char Level No No Yes No No No No SL No SL No No No SL No No SL No SL No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No No No SL No No SL No No No No No No No No No No No No No No Yes No No No No Ratio Boeing Soil Char Level 2.32E‐01 4.42E‐01 1.12E+00 4.87E‐01 7.60E‐01 4.88E‐02 No SL No SL 2.69E‐02 1.24E‐03 No SL 3.48E‐04 No SL No SL 7.19E‐02 2.56E‐04 1.00E‐02 5.11E‐03 2.09E‐01 1.77E‐03 6.46E‐02 2.88E‐04 3.96E‐05 1.91E‐03 6.36E‐03 9.55E‐04 5.43E‐03 5.43E‐02 5.43E‐03 2.84E‐04 5.43E‐03 1.75E‐03 1.86E‐02 3.89E‐05 2.36E‐03 5.43E‐03 1.44E‐04 1.62E‐03 1.75E‐03 No SL No SL 6.05E‐02 4.50E‐03 4.50E‐03 4.50E‐03 6.30E+00 9.29E‐03 No SL 7.19E‐02 2.56E‐04 1.00E‐02 5.11E‐03 2.09E‐01 1.77E‐03 6.46E‐02 2.88E‐04 3.96E‐05 1.91E‐03 6.36E‐03 9.55E‐04 5.43E‐03 5.43E‐02 5.43E‐03 2.84E‐04 5.43E‐03 1.75E‐03 1.86E‐02 3.89E‐05 2.36E‐03 5.43E‐03 8.22E‐05 1.62E‐03 1.75E‐03 No SL No SL No SL No SL 2.86E‐02 2.48E‐03 No SL 7.30E‐03 No SL 6.54E‐01 8.00E‐01 2.05E‐01 2.35E‐01 5.92E‐01 3.34E‐01 8.37E‐01 4.90E‐01 3.84E‐01 3.34E‐01 4.70E‐01 4.95E‐01 1.67E‐01 5.00E‐01 1.08E+00 3.79E‐01 3.45E‐01 2.29E‐01 2.28E‐01 SCL Basis Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 19 19 19 19 19 2.1 2.4 5.9 1.2 5.3 1.2 5.9 6 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.3 1.3 2.6 6.3 6.3 6.3 6.3 13 1.3 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.3 1.3 2.5 31.4 1.3 5.8 1.3 6.3 12.6 12.5 0.625 0.313 6.25 0.938 0.625 2.5 0.625 62.5 62.5 0.625 2.5 6.25 0.25 0.5 0.125 0.25 0.25 0.125 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 8.9 3.7 3.7 3.7 5.5 1.3 0.12 1.2 0.48 2.1 0.48 0.12 1.9 0.26 7.6 7.6 7.6 7.6 7.6 7.6 0.84 0.84 0.84 0.84 0.42 0.42 0.84 0.84 0.84 0.84 0.84 0.42 0.84 0.84 0.84 0.84 0.84 0.84 0.84 0.26 0.26 1.5 2.5 2.5 2.5 2.5 5 0.25 7.5 7.5 7.5 7.5 7.5 7.5 0.84 0.84 0.84 0.84 0.42 0.42 0.84 0.84 0.84 0.84 0.84 0.42 0.84 0.84 0.84 0.84 0.84 0.84 0.84 0.25 0.25 0.13 6.3 0.5 2.2 0.5 0.13 4 9.64 0.0413 0.0838 1.04 0.11 0.113 0.69 0.104 16.9 20.9 0.138 0.25 1.04 0.085 0.105 0.0575 0.183 0.0183 0.065 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S003 ELBS2006S004 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:10 6/13/13 9:20 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 9 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 10 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Metals Metals Metals Metals VOCs Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs Analysis  Method 6020 6020 6020 6020 8315A 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8082 8082 8082 8082 8082 8082 8082 Analyte Nickel Selenium Silver Thallium Formaldehyde Arsenic DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Page 58 of 108 CAS Number 7440020 7782492 7440224 7440280 50000 7440382 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 37324235 11100144 12674112 11104282 11141165 53469219 12672296 Result  Value 27.8 0.125 0.241 0.346 2.5 17.6 1.67 1.12 1.62 5.53 33.6 0.419 0.799 0.528 0.321 1.55 0.305 1.58 5.68 0.438 0.341 0.246 0.208 0.0714 14.2 63.5 7.01 12.5 17.4 378 25.6 5.92 34.8 1.31 310 310 620 310 620 310 310 310 310 310 310 420 310 2100 2100 310 310 310 1.8 1.8 37 18 93 12 18 25 2600 2600 0.1 1.3 1.2 4.3 0.41 0.16 2.1 0.18 26800 132 0.898 6.36 29 7.02 24.8 311 2600 134 50.5 54.2 4.71 0.0859 5.56 0.236 11.4 8.15 0.482 17.5 0.188 0.0516 0.285 0.0103 17 17 17 17 17 17 17 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 27.8 mg/kg 0.5 mg/kg 0.241 mg/kg 0.346 mg/kg 2.5 mg/kg 17.6 mg/kg 0.00000167 mg/kg 0.00000112 mg/kg 0.00000162 mg/kg 0.00000553 mg/kg 0.0000336 mg/kg 0.00000499 mg/kg 0.000000799 mg/kg 0.00000499 mg/kg 0.00000499 mg/kg 0.00000155 mg/kg 0.00000499 mg/kg 0.00000158 mg/kg 0.00000568 mg/kg 0.000000438 mg/kg 0.000000341 mg/kg 0.000000246 mg/kg 0.00000104 mg/kg 0.000000998 mg/kg 0.00000499 mg/kg 0.0000635 mg/kg 0.00000499 mg/kg 0.00000499 mg/kg 0.0000174 mg/kg 0.000378 mg/kg 0.00000499 mg/kg 0.00000499 mg/kg 0.000000998 mg/kg 0.000000998 mg/kg 0.31 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.42 mg/kg 0.31 mg/kg 2.1 mg/kg 2.1 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.037 mg/kg 0.018 mg/kg 0.093 mg/kg 0.012 mg/kg 0.018 mg/kg 0.025 mg/kg 2.6 mg/kg 2.6 mg/kg 2.1 mg/kg 1.3 mg/kg 1.2 mg/kg 4.3 mg/kg 1 mg/kg 0.16 mg/kg 5.1 mg/kg 0.49 mg/kg 26800 mg/kg 132 mg/kg 0.898 mg/kg 6.36 mg/kg 29 mg/kg 7.02 mg/kg 24.8 mg/kg 311 mg/kg 2600 mg/kg 134 mg/kg 50.5 mg/kg 54.2 mg/kg 4.71 mg/kg 0.2 mg/kg 5.56 mg/kg 0.236 mg/kg 11.4 mg/kg 8.15 mg/kg 0.482 mg/kg 17.5 mg/kg 0.188 mg/kg 0.0516 mg/kg 0.285 mg/kg 0.103 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg Detected Y N Y Y N Y Y Y Y Y Y N Y N N Y N Y Y Y Y Y N N N Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N N N N N N N Project  Qual  Code Validation Note U U UJ J UJ UJ J UJ J J J J U U UJ UJ UJ UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U J J U J U U F F, B M, F, B F, B M, F M, F, B M F, B F, B F F F, B B F B, M, F F, B M, F, B M, F, B F, B F, B M, F, B M, F, B M, B M, F, B L F F F J U B B J J U U U U U U U U Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 64.2 No 4.33E‐01 Background 1 No 5.00E‐01 MRL 0.99 No 2.43E‐01 Ecological RBSL 0.761 No 4.55E‐01 Suburban Residential RBSL 43 No 5.81E‐02 Ecological RBSL 24.2 No 7.27E‐01 Background 0.0000057 No 2.93E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 2.88E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.37E‐01 Ecological RBSL 0.3 Yes 1.03E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.03E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 3.82E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.03E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.75E‐04 Ecological RBSL 0.55 No 3.27E‐03 Ecological RBSL 1.1 No 3.36E‐02 Ecological RBSL 6.2 No 2.90E‐03 Ecological RBSL 39 No 2.38E‐03 Ecological RBSL 14 No 8.57E‐04 Ecological RBSL 0.79 No 2.28E‐02 Ecological RBSL 0.18 No 1.39E‐01 Ecological RBSL 3.3 No 7.88E‐01 MRL 3.3 No 7.88E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 3.43E‐02 Ecological RBSL 2340 No 1.84E‐03 Ecological RBSL ‐‐ No SL No SL 863.2 No 1.85E‐04 Background ‐‐ No SL No SL 0.5 No 9.80E‐01 MRL 37900 No 7.07E‐01 Background 203.8 No 6.48E‐01 Background 4.8 No 1.87E‐01 Ecological RBSL 22 No 2.89E‐01 Ecological RBSL 60.11 No 4.82E‐01 Background 26.18 No 2.68E‐01 Background 64.4 No 3.85E‐01 Background 723 No 4.30E‐01 Background 7524 No 3.46E‐01 Background 754 No 1.78E‐01 Background 111.8 No 4.52E‐01 Background 153 No 3.54E‐01 Background 10.64 No 4.43E‐01 Background 0.5 No 4.00E‐01 MRL 24.2 No 2.30E‐01 Background 0.435 No 5.43E‐01 Background 42 No 2.71E‐01 Background 33.9 No 2.40E‐01 Background 1.642 No 2.94E‐01 Background 64.2 No 2.73E‐01 Background 1 No 1.88E‐01 MRL 0.99 No 5.21E‐02 Ecological RBSL 0.761 No 3.75E‐01 Suburban Residential RBSL 0.87 No 1.18E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.42E‐01 Ecological RBSL 0.18 No 9.44E‐02 Ecological RBSL 0.082 No 2.07E‐01 Ecological RBSL 0.043 No 3.95E‐01 Ecological RBSL 0.017 No 1.00E+00 MRL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 0.5 0.5 0.125 0.125 2.5 0.489 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.193 0.125 0.025 0.0375 1.5 0.103 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 1.04 0.998 4.99 4.99 4.99 4.99 9.98 9.98 4.99 4.99 0.998 0.998 310 310 620 310 620 310 310 310 310 310 310 420 310 2100 2100 310 310 310 1.8 1.8 37 18 93 12 18 25 2600 2600 2.1 5.1 1 4.4 1 5.1 5.1 0.49 9.98 0.499 0.25 4.99 0.749 0.499 2 0.499 49.9 49.9 0.499 2 4.99 0.2 0.399 0.0998 0.2 0.2 0.0998 0.399 0.399 0.0998 0.0998 0.103 17 17 17 17 17 17 17 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0235 0.0741 0.0347 0.0343 0.0572 0.0343 0.0617 0.0409 0.0636 0.0531 0.0772 0.0328 0.0517 0.208 0.0361 0.0279 0.0741 0.0353 0.0607 0.0299 0.0476 0.0524 0.0772 0.106 0.0361 100 100 210 100 210 100 100 210 260 160 210 260 100 1600 1600 130 100 160 0.85 0.78 12 6.4 46 4.1 9.3 9.3 790 780 0.1 1 0.41 1.8 0.41 0.1 1.6 0.18 7.2 0.0329 0.0669 0.839 0.16 0.0988 0.34 0.0829 8.33 16.7 0.13 0.2 0.839 0.0859 0.0839 0.0459 0.0959 0.016 0.0499 0.0759 0.0998 0.026 0.03 0.0103 3.4 3.4 3.7 4.7 8.2 3.4 3.4 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N Y N N N N N Y Y Y Y N Y N N Y N N N N N N Y N N Y N Y N N N N N N N N Y N N N N Y Y N N Y N N N N N N N N N N Y Y N Y Y Y N Y Y Y Y Y Y Y Y Y N Y N Y N Y Y Y N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date Matrix  Type 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:00 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Lab Repeat Analysis Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 6010B 9012B 9056 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Analyte Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans sym‐Trinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 4‐Amino‐2,6‐Dinitrotoluene HMX 1,3‐Dinitrobenzene 3‐Nitrotoluene Nitrobenzene 2‐Nitrotoluene PETN 4‐Nitrotoluene RDX Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Phosphorus Cyanides Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Antimony Barium Boron Calcium Chromium Cobalt Iron Manganese Potassium Silver Sodium Strontium Tin Page 59 of 108 CAS Number 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 51207319 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 99354 118967 6629294 121142 59229753 606202 35572782 19406510 2691410 99650 99081 98953 88722 78115 99990 121824 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 7723140 57125 24959679 16887006 16984488 NO3 NO2 14265442 14808798 7440360 7440393 7440428 7440702 7440473 7440484 7439896 7439965 7440097 7440224 7440235 7440246 7440315 Result  Value 27 17 1.8 1.8 1.8 0.86 0.86 1 18 0.86 1.8 1.8 0.86 1.8 1.8 1.8 1.9 0.86 0.86 0.86 1.8 6.9 34 2.31 1.81 3.3 0.352 18.1 124 1.56 1.18 2.02 0.75 4.37 0.98 5.27 3.66 1.22 0.807 0.389 0.225 0.79 67.8 1690 259 57.5 35.1 16.5 5.98 17.6 1.61 10.9 150 150 1990 150 1990 150 150 150 150 150 150 150 150 500 150 150 150 5.35 5.35 5.35 5.35 107 5.35 5.35 5.35 1070 1070 184 0.0813 2.09 3.4 1.71 2.1 0.353 0.717 3.42 1.08 131 7.23 3700 20.3 6.6 20600 302 2080 0.148 86.8 31.5 0.306 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.027 mg/kg 0.017 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.001 mg/kg 0.018 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.0069 mg/kg 0.034 mg/kg 0.00000231 mg/kg 0.00000181 mg/kg 0.0000033 mg/kg 0.00000093 mg/kg 0.0000181 mg/kg 0.000124 mg/kg 0.00000465 mg/kg 0.00000465 mg/kg 0.00000202 mg/kg 0.00000465 mg/kg 0.00000437 mg/kg 0.00000465 mg/kg 0.00000527 mg/kg 0.00000366 mg/kg 0.00000465 mg/kg 0.00000465 mg/kg 0.00000465 mg/kg 0.00000093 mg/kg 0.00000079 mg/kg 0.0000678 mg/kg 0.00169 mg/kg 0.000259 mg/kg 0.0000575 mg/kg 0.0000351 mg/kg 0.00000465 mg/kg 0.00000598 mg/kg 0.00000465 mg/kg 0.00000093 mg/kg 0.0000109 mg/kg 0.15 mg/kg 0.15 mg/kg 1.99 mg/kg 0.15 mg/kg 1.99 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.5 mg/kg 0.15 mg/kg 0.15 mg/kg 0.15 mg/kg 0.00535 mg/kg 0.00535 mg/kg 0.00535 mg/kg 0.00535 mg/kg 0.107 mg/kg 0.00535 mg/kg 0.00535 mg/kg 0.00535 mg/kg 1.07 mg/kg 1.07 mg/kg 184 mg/kg 0.243 mg/kg 2.09 mg/kg 3.4 mg/kg 1.71 mg/kg 2.1 mg/kg 1.07 mg/kg 2.14 mg/kg 4.28 mg/kg 1.08 mg/kg 131 mg/kg 7.23 mg/kg 3700 mg/kg 20.3 mg/kg 6.6 mg/kg 20600 mg/kg 302 mg/kg 2080 mg/kg 0.148 mg/kg 86.8 mg/kg 31.5 mg/kg 1.02 mg/kg Detected Y N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y N N Y N Y N Y Y N N N N Y Y Y Y Y Y N Y N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y Y Y Y N N N Y Y Y Y Y Y Y Y Y Y Y Y N Project  Qual  Code Validation Note U U U U U U U U U U U U U U U U U U U U U U U U UJ J U J U J U U U U J UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U J U J U U U D, B F, B F, B F, B F, B, M F, B F, B B B F, B F, B F, B B, F F, B F, B B F, B F, B F, B F, B F, B F, B, M F, B F, B, M F, B, M B Q F F J U Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.039 No 6.92E‐01 Ecological RBSL 0.025 No 6.80E‐01 Ecological RBSL 0.0051 No 3.53E‐01 Ecological RBSL 0.004164 No 4.32E‐01 Background 0.006101 No 2.95E‐01 Background 0.0348 No 2.47E‐02 Suburban Residential RBSL 0.073 No 1.18E‐02 Ecological RBSL 0.394 No 2.54E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.28E‐02 Ecological RBSL 0.013 No 1.38E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 3.91E‐03 Ecological RBSL 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.15E‐02 Ecological RBSL 0.087 No 9.89E‐03 Ecological RBSL 0.0017 No 5.06E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.76E‐03 Ecological RBSL 0.493 No 6.90E‐02 Suburban Residential RBSL 0.0000057 No 4.05E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 5.86E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 5.00E‐01 MRL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 5.00E‐01 MRL ‐‐ No SL No SL 110 No 1.36E‐03 Ecological RBSL 0.92 No 1.63E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 5.00E‐01 Ecological RBSL ‐‐ No SL No SL 4.8 No 1.11E‐03 Ecological RBSL 0.55 No 9.73E‐03 Ecological RBSL 1.1 No 4.86E‐03 Ecological RBSL 6.2 No 8.63E‐04 Ecological RBSL 39 No 2.74E‐03 Ecological RBSL 14 No 3.82E‐04 Ecological RBSL 0.79 No 6.77E‐03 Ecological RBSL 0.18 No 2.97E‐02 Ecological RBSL 3.3 No 3.24E‐01 MRL 3.3 No 3.24E‐01 MRL ‐‐ No SL No SL 0.5 No 4.86E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 4.89E‐02 Ecological RBSL 2340 No 8.97E‐04 Ecological RBSL ‐‐ No SL No SL 863.2 No 2.48E‐03 Background ‐‐ No SL No SL 0.5 Yes 2.16E+00 MRL 203.8 No 6.43E‐01 Background 22 No 3.29E‐01 Ecological RBSL ‐‐ No SL No SL 60.11 No 3.38E‐01 Background 26.18 No 2.52E‐01 Background ‐‐ No SL No SL 723 No 4.18E‐01 Background 7524 No 2.76E‐01 Background 0.99 No 1.49E‐01 Ecological RBSL 754 No 1.15E‐01 Background 1210 No 2.60E‐02 Ecological RBSL 31 No 3.29E‐02 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 17 17 1.8 1.8 1.8 0.86 0.86 1 18 0.86 1.8 1.8 0.86 1.8 1.8 1.8 1.9 0.86 0.86 0.86 1.8 6.9 34 0.93 4.65 4.65 4.65 4.65 4.65 4.65 4.65 4.65 4.65 4.65 4.65 4.65 4.65 0.93 0.93 9.3 9.3 4.65 4.65 4.65 4.65 4.65 4.65 0.93 0.93 150 150 1990 150 1990 150 150 150 150 150 150 150 150 500 150 150 150 5.35 5.35 5.35 5.35 107 5.35 5.35 5.35 1070 1070 15.3 0.243 2.14 2.14 1.07 1.07 1.07 2.14 4.28 1.02 0.51 5.1 25.5 0.51 0.51 25.5 1.02 25.5 0.51 25.5 0.51 1.02 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL 3.4 5 0.34 0.97 0.34 0.34 0.18 0.31 4.1 0.19 1.2 0.34 0.23 0.51 0.39 0.34 0.34 0.18 0.31 0.32 0.34 1.8 11 50 50 498 50 657 50 50 50 50 50 50 50 50 82.5 50 50 50 1.78 1.78 1.78 1.78 37.4 2.14 2.42 1.78 246 214 5.1 0.0813 0.717 0.717 0.353 0.353 0.353 0.717 1.42 0.336 0.102 1.02 8.16 0.153 0.153 8.16 0.204 6.52 0.102 7.14 0.102 0.306 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N Y N Y Y Y N Y Y Y N Y Y Y Y Y N N N N N Y Y Y Y Y Y N Y Y N Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y Y N N Y N N Y N Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S001SP ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S002 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 ELBS2007S001 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:10 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:20 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH Analysis  Method 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 7199 8315A 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Titanium Vanadium Zinc Aluminum Arsenic Beryllium Cadmium Copper Lead Lithium Magnesium Molybdenum Nickel Selenium Thallium Zirconium Mercury Aroclor 1268 Aroclor 5432 Aroclor 5442 Aroclor 5460 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1262 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan I Endosulfan II Endosulfan sulfate Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Methoxychlor Mirex Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Page 60 of 108 CAS Number 7440326 7440622 7440666 7429905 7440382 7440417 7440439 7440508 7439921 7439932 7439954 7439987 7440020 7782492 7440280 7440677 7439976 11100144 63496311 12642238 11126424 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 72548 72559 50293 309002 319846 319857 57749 319868 60571 959988 33213659 1031078 72208 7421934 53494705 58899 76448 1024573 72435 2385855 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 Result  Value 709 45.4 46.4 22900 4.14 0.74 0.494 10.7 10.7 19.4 3770 0.481 17.2 0.335 0.302 2.64 0.00775 3.56 17.8 17.8 17.8 3.56 3.56 3.56 3.56 3.56 3.56 3.56 3.56 1.42 1.42 1.42 0.711 0.711 0.711 8.89 0.711 1.42 0.711 1.42 1.42 1.42 1.42 1.42 0.711 0.711 0.711 7.11 0.711 17.8 11 4.4 130 11 150 25 19 19 19 19 9.6 1.7 0.94 1.2 17 2.1 130 1200 740 1000 230 520 1500 96 2300 15 260 1.7 910 2500 4.2 0.4 2 0.00393 0.00393 0.0106 5.4 5.4 5.1 5.4 10 19 19 19 19 19 19 1.8 1.8 1.8 1.8 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 709 45.4 46.4 22900 4.14 0.74 0.494 10.7 10.7 19.4 3770 0.481 17.2 1.02 0.302 2.64 0.00775 0.00356 0.0178 0.0178 0.0178 0.00356 0.00356 0.00356 0.00356 0.00356 0.00356 0.00356 0.00356 0.00142 0.00142 0.00142 0.000711 0.000711 0.000711 0.00889 0.000711 0.00142 0.000711 0.00142 0.00142 0.00142 0.00142 0.00142 0.000711 0.000711 0.000711 0.00711 0.000711 0.0178 11 4.4 130 11 150 0.019 0.019 0.019 0.019 0.019 0.0096 0.0017 0.00094 0.0012 0.017 0.0021 0.13 1.2 0.74 1 0.23 0.52 1.5 0.096 2.3 0.015 0.26 0.0017 0.91 2.5 0.0042 0.41 2 3.93E‐09 3.93E‐09 1.06E‐08 5.4 5.4 5.1 5.4 10 0.019 0.019 0.019 0.019 0.019 0.019 0.0018 0.0018 0.0018 0.0018 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N Y N N N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N Y Y Y N N Y N Y N N N N N N N N N N Project  Qual  Code Validation Note F J J U J J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J B Q Q Q S S S, L S S S S S S S S S S, L S S S S S S S S U U U U U U J U J J F F, Original Result = 9.3 J L J U U U U U J U J U U U U U U U U U U B F F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 1865 No 3.80E‐01 Background 111.8 No 4.06E‐01 Background 153 No 3.03E‐01 Background 37900 No 6.04E‐01 Background 24.2 No 1.71E‐01 Background 4.8 No 1.54E‐01 Ecological RBSL 0.435 Yes 1.14E+00 Background 42 No 2.55E‐01 Background 33.9 No 3.16E‐01 Background 64.4 No 3.01E‐01 Background ‐‐ No SL No SL 1.642 No 2.93E‐01 Background 64.2 No 2.68E‐01 Background 1 Yes 1.02E+00 MRL 0.761 No 3.97E‐01 Suburban Residential RBSL 10.64 No 2.48E‐01 Background 0.87 No 8.91E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.05 No 3.56E‐01 MRL 0.12 No 2.97E‐02 Ecological RBSL 0.18 No 1.98E‐02 Ecological RBSL 0.082 No 4.34E‐02 Ecological RBSL 0.043 No 8.28E‐02 Ecological RBSL 0.017 No 2.09E‐01 MRL 0.039 No 9.13E‐02 Ecological RBSL 0.025 No 1.42E‐01 Ecological RBSL ‐‐ No SL No SL 0.0051 No 2.78E‐01 Ecological RBSL 0.004164 No 3.41E‐01 Background 0.006101 No 2.33E‐01 Background 0.0348 No 2.04E‐02 Suburban Residential RBSL 0.073 No 9.74E‐03 Ecological RBSL 0.394 No 1.80E‐03 Suburban Residential RBSL 1.1 No 8.08E‐03 Ecological RBSL 0.067 No 1.06E‐02 Ecological RBSL 0.013 No 1.09E‐01 Ecological RBSL 0.22 No 3.23E‐03 Ecological RBSL 0.22 No 6.45E‐03 Ecological RBSL 0.23 No 6.17E‐03 Ecological RBSL 0.0079 No 1.80E‐01 Ecological RBSL 0.0092 No 1.54E‐01 Ecological RBSL 0.0086 No 1.65E‐01 Ecological RBSL 0.075 No 9.48E‐03 Ecological RBSL 0.087 No 8.17E‐03 Ecological RBSL 0.0017 No 4.18E‐01 MRL 2.5 No 2.84E‐03 Ecological RBSL 0.0328 No 2.17E‐02 Suburban Residential RBSL 0.493 No 3.61E‐02 Suburban Residential RBSL 1400 No 7.86E‐03 1400 No 3.14E‐03 1400 No 9.29E‐02 1 Yes 1.10E+01 1400 No 1.07E‐01 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 7.38E‐04 Ecological RBSL 0.0325 No 5.23E‐02 Suburban Residential RBSL 7.29 No 1.29E‐04 Suburban Residential RBSL 53 No 2.26E‐05 Ecological RBSL 1.1 No 1.55E‐02 Ecological RBSL 0.33 No 6.36E‐03 Ecological RBSL 2.2 No 5.91E‐02 Ecological RBSL 0.387 Yes 3.10E+00 Suburban Residential RBSL 0.0387 Yes 1.91E+01 Suburban Residential RBSL 0.387 Yes 2.58E+00 Suburban Residential RBSL 7.4 No 3.11E‐02 Ecological RBSL 0.387 Yes 1.34E+00 Suburban Residential RBSL 1.2 Yes 1.25E+00 Ecological RBSL 0.113 No 8.50E‐01 Suburban Residential RBSL 54 No 4.26E‐02 Ecological RBSL 0.89 No 1.69E‐02 Ecological RBSL 0.387 No 6.72E‐01 Suburban Residential RBSL 14.6 No 1.16E‐04 Suburban Residential RBSL 1.3 No 7.00E‐01 Ecological RBSL 1.2 Yes 2.08E+00 Ecological RBSL 0.5 No 8.40E‐03 Ecological RBSL 1.29 No 3.18E‐01 Suburban Residential RBSL 43 No 4.65E‐02 Ecological RBSL 0.0000057 No 6.89E‐04 Ecological RBSL No SL No SL ‐‐ 0.000000563 No 1.88E‐02 Background 1400 No 3.86E‐03 1400 No 3.86E‐03 1400 No 3.64E‐03 1 Yes 5.40E+00 1400 No 7.14E‐03 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 1.46E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 0.51 0.51 1.02 102 1.02 0.102 0.203 0.203 0.406 2.03 6.09 0.203 0.406 1.02 0.406 0.406 0.0111 3.56 17.8 17.8 17.8 3.56 3.56 3.56 3.56 3.56 3.56 3.56 3.56 1.42 1.42 1.42 0.711 0.711 0.711 8.89 0.711 1.42 0.711 1.42 1.42 1.42 1.42 1.42 0.711 0.711 0.711 7.11 0.711 17.8 11 11 11 11 21 19 19 19 19 19 19 1.7 1.7 1.7 1.7 1.7 1.7 87 87 87 1.7 87 87 1.7 87 1.7 1.7 1.7 87 87 4.2 0.41 2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 0.102 0.102 0.408 30.5 0.203 0.0203 0.0203 0.067 0.102 0.406 2.03 0.0609 0.102 0.335 0.0609 0.102 0.00371 1.18 3.56 3.56 3.56 1.18 1.18 1.18 1.18 1.18 1.18 1.18 1.18 0.356 0.356 0.356 0.178 0.178 0.178 1.78 0.178 0.356 0.178 0.356 0.356 0.356 0.356 0.356 0.178 0.178 0.178 1.78 0.178 5.92 4.2 4.2 4.2 4.2 8.5 6.2 6.2 6.2 6.2 6.2 6.2 0.69 0.69 0.69 0.69 0.35 0.35 35 35 35 0.69 35 17 0.69 35 0.69 0.69 0.69 35 35 2.2 0.14 1.2 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 5.4 5.4 5.4 5.4 11 19 19 19 19 19 19 1.8 1.8 1.8 1.8 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 2.2 2.2 2.2 2.2 4.3 6.4 6.4 6.4 6.4 6.4 6.4 0.72 0.72 0.72 0.72 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N Y N Y N Y N N N Y N Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Sample  Bottom  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7199 Analyte Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Hexavalent Chromium Page 61 of 108 CAS Number 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 18540299 Result  Value 1.8 1.8 1.1 0.75 0.87 1.8 1.8 1.1 1.8 2.2 1.8 1.8 1.8 1.5 2.2 0.0885 0.635 0.0346 0.0477 0.0314 0.025 0.0608 0.028 0.0443 0.264 0.0488 0.00972 0.0223 0.0329 0.0247 0.306 1.32 0.317 0.622 0.239 4.99 1.23 0.393 3.16 0.0983 310 310 620 310 620 310 310 310 310 310 310 420 310 2100 2100 310 310 310 1.8 1.8 39 18 98 13 18 26 2700 2700 0.11 1.3 1.7 1.9 0.43 0.11 11.9 5.2 0.19 18000 99 0.713 5.29 22.3 5.41 25.8 316 1320 300 39.8 38.1 3.79 0.093 22.5 0.141 9.09 6.68 0.17 18.1 0.108 0.0481 0.218 0.28 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.0018 mg/kg 0.0018 mg/kg 0.0011 mg/kg 0.00075 mg/kg 0.00087 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0011 mg/kg 0.0018 mg/kg 0.0022 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0015 mg/kg 0.0022 mg/kg 0.00000532 mg/kg 0.000000635 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.000000028 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000106 mg/kg 0.00000106 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.0000106 mg/kg 0.00000499 mg/kg 0.00000532 mg/kg 0.00000532 mg/kg 0.00000106 mg/kg 0.00000106 mg/kg 0.31 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.42 mg/kg 0.31 mg/kg 2.1 mg/kg 2.1 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.039 mg/kg 0.018 mg/kg 0.098 mg/kg 0.013 mg/kg 0.018 mg/kg 0.026 mg/kg 2.7 mg/kg 2.7 mg/kg 2.2 mg/kg 1.3 mg/kg 1.7 mg/kg 4.9 mg/kg 1.1 mg/kg 5.4 mg/kg 11.9 mg/kg 0.0052 mg/kg 0.52 mg/kg 18000 mg/kg 99 mg/kg 0.713 mg/kg 5.29 mg/kg 22.3 mg/kg 5.41 mg/kg 25.8 mg/kg 316 mg/kg 1320 mg/kg 300 mg/kg 39.8 mg/kg 38.1 mg/kg 3.79 mg/kg 0.216 mg/kg 22.5 mg/kg 0.141 mg/kg 9.09 mg/kg 6.68 mg/kg 0.17 mg/kg 18.1 mg/kg 0.432 mg/kg 0.0481 mg/kg 0.218 mg/kg 0.45 mg/kg Detected N N Y Y Y N N Y N Y N N N Y Y N Y N N N N N Y N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y N N N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y N Project  Qual  Code Validation Note U U J J J U U J U U U U J L U J U UJ UJ UJ UJ J U UJ UJ U U U U UJ UJ UJ UJ U J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U J F F, B F, B M, F, B M, F M, F, B M F, B M, F, B M, F F F, B B F M, F, B M, F, B M, F, B M, F, B F, B F, B M, F, B M, F, B M, B M, F, B L U U U F U J F F J U B B U J U B Boeing Soil Char Level  (mg/kg) 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 1.29 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL No Yes No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 5.45E‐03 8.18E‐04 2.84E‐03 1.94E‐02 2.25E‐03 2.43E‐04 4.65E‐03 9.17E‐04 1.59E‐02 4.07E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.15E‐03 1.83E‐03 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.37E‐01 1.03E+00 No SL No SL No SL No SL 1.03E+00 No SL No SL No SL No SL 3.82E‐03 No SL No SL No SL 1.03E+00 No SL No SL 3.75E‐04 3.27E‐03 3.55E‐02 2.90E‐03 2.51E‐03 9.29E‐04 2.28E‐02 1.44E‐01 8.18E‐01 8.18E‐01 No SL No SL 4.86E‐02 2.09E‐03 No SL 6.26E‐03 No SL 1.04E‐02 1.04E+00 4.75E‐01 4.86E‐01 1.49E‐01 2.40E‐01 3.71E‐01 2.07E‐01 4.01E‐01 4.37E‐01 1.75E‐01 3.98E‐01 3.56E‐01 2.49E‐01 3.56E‐01 4.32E‐01 9.30E‐01 3.24E‐01 2.16E‐01 1.97E‐01 1.04E‐01 2.82E‐01 4.32E‐01 4.86E‐02 2.86E‐01 3.49E‐01 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background Ecological RBSL MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5.32 5.32 5.32 5.32 5.32 5.32 5.32 5.32 5.32 5.32 5.32 5.32 5.32 1.06 1.06 5.32 5.32 5.32 5.32 10.6 10.6 5.32 5.32 1.06 1.06 310 310 620 310 620 310 310 310 310 310 310 420 310 2100 2100 310 310 310 1.8 1.8 39 18 98 13 18 26 2700 2700 2.2 5.4 1.1 4.9 1.1 5.4 5.4 4.4 0.52 10.8 0.54 0.27 5.4 0.811 0.54 2.2 0.54 54 54 0.54 2.16 5.4 0.216 0.432 0.108 0.216 0.216 0.108 0.432 0.432 0.108 0.108 0.45 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL 0.36 0.36 0.72 0.72 0.72 0.72 0.72 0.36 0.72 0.72 0.72 0.72 0.72 0.72 0.72 0.0109 0.0368 0.0181 0.0118 0.0211 0.0114 0.0223 0.0141 0.0231 0.0224 0.0355 0.00972 0.0223 0.0329 0.0247 0.0136 0.0368 0.0116 0.0222 0.0288 0.0273 0.0224 0.0355 0.0329 0.0247 100 100 210 100 210 100 100 210 260 160 210 260 100 1600 1600 130 100 160 0.89 0.82 13 7.5 48 4.4 9.8 9.8 830 1100 0.11 1.1 0.43 1.9 0.43 0.11 1.7 2.3 0.19 7.79 0.0357 0.0724 0.908 0.173 0.107 0.37 0.0897 9.01 18.1 0.141 0.216 0.908 0.093 0.0908 0.0497 0.104 0.0173 0.054 0.0821 0.108 0.0281 0.0324 0.16 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2007S003 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/19/13 9:30 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs VOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 8260B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde Xylenes, Total 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Page 62 of 108 CAS Number 7439976 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1330207 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 Result  Value 0.0109 19 19 19 19 19 19 19 19 19 1.8 1.8 1.8 0.9 0.9 1.1 18 0.9 1.8 1.8 0.9 1.8 1.8 1.8 2 0.9 0.9 0.9 1.8 7.3 36 2.2 5 5 5 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 0.37 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 20 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Result  Value  Units mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.109 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.0018 0.0018 0.0018 0.0009 0.0009 0.0011 0.018 0.0009 0.0018 0.0018 0.0009 0.0018 0.0018 0.0018 0.002 0.0009 0.0009 0.0009 0.0018 0.0073 0.036 2.2 0.005 0.005 0.005 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.00037 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.01 0.01 0.02 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note H L F F L L, L Boeing Soil Char Level  (mg/kg) 0.87 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 0.075 0.087 0.0017 0.0328 2.5 0.493 43 3.4 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 7.28 22.3 Exceeds Boeing Soil Char Level No No SL No SL No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No SL No No No No No No SL No No No SL No No SL No No Ratio Boeing Soil Char Level 1.25E‐01 No SL No SL 1.58E‐01 1.06E‐01 2.32E‐01 4.42E‐01 1.12E+00 4.87E‐01 7.60E‐01 3.53E‐01 4.32E‐01 2.95E‐01 2.59E‐02 1.23E‐02 2.79E‐03 1.64E‐02 1.34E‐02 1.38E‐01 7.83E‐03 4.09E‐03 8.18E‐03 2.28E‐01 1.96E‐01 2.33E‐01 1.20E‐02 1.03E‐02 5.29E‐01 5.49E‐02 2.92E‐03 7.30E‐02 5.12E‐02 1.47E‐03 5.00E‐04 2.27E‐01 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 3.08E‐04 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 1.74E‐03 2.03E‐06 1.74E‐02 2.27E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 1.00E+00 4.35E‐04 2.22E‐03 4.35E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 6.87E‐04 2.24E‐04 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 0.109 19 19 19 19 19 19 19 19 19 1.8 1.8 1.8 0.9 0.9 1.1 18 0.9 1.8 1.8 0.9 1.8 1.8 1.8 2 0.9 0.9 0.9 1.8 7.3 36 2.2 5 5 5 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 20 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 RL Units MDL mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0109 3.6 3.6 3.9 5 8.7 3.6 3.6 3.6 5.3 0.36 0.36 0.36 0.36 0.18 0.33 4.4 0.2 0.36 0.36 0.24 0.36 0.36 0.36 0.36 0.18 0.33 0.21 0.36 1.8 12 1.3 1 1 2 6.5 6.5 6.5 6.5 6.5 6.5 0.72 0.72 0.72 0.72 0.36 0.36 0.72 0.72 0.72 0.72 0.72 0.36 0.72 0.72 0.72 0.72 0.72 0.72 0.72 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 7 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 MDL  Units mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y N N N N N N N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008D002 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S001 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:30 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals VOCs Inorganics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 7199 8315A 9045C 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8260B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Hexavalent Chromium Formaldehyde pH 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Xylenes, Total 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Page 63 of 108 CAS Number 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 18540299 50000 E‐10139 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1330207 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 Result  Value 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 51 5 5 5 5 5 5 5 5 5 0.26 2.2 8.16 290 290 570 290 570 290 290 290 290 290 290 380 290 1900 1900 290 290 290 1.8 1.8 37 18 93 12 18 25 2600 2600 0.1 8.4 0.4 9.7 0.4 0.18 5.8 0.18 1.8 1.8 0.99 0.86 0.86 1 18 0.86 1.8 1.8 0.86 1.8 1.8 1.8 1.9 0.86 0.86 0.86 0.4 7 34 5 5 5 20 20 20 20 20 20 1.8 1.8 1.8 1.8 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg pH Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.005 0.005 0.005 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.051 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.42 2.2 8.16 0.29 0.29 0.57 0.29 0.57 0.29 0.29 0.29 0.29 0.29 0.29 0.38 0.29 1.9 1.9 0.29 0.29 0.29 0.0018 0.0018 0.037 0.018 0.093 0.012 0.018 0.025 2.6 2.6 2 8.4 1 9.7 1 0.18 5 0.51 0.0018 0.0018 0.00099 0.00086 0.00086 0.001 0.018 0.00086 0.0018 0.0018 0.00086 0.0018 0.0018 0.0018 0.0019 0.00086 0.00086 0.00086 0.0004 0.007 0.034 0.005 0.005 0.005 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.0018 0.0018 0.0018 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N Y N N N N Y N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U U J U J U U U U J U U U U U U U U U U U U U U U J U U U U U U U U U U U U U U U Validation Note B L L L F Q Q F L F F Boeing Soil Char Level  (mg/kg) 41 ‐‐ 2.31 1.3 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 ‐‐ ‐‐ ‐‐ 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 1.29 43 ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 0.075 0.087 0.0017 0.0328 2.5 0.493 3.4 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 Exceeds Boeing Soil Char Level No No SL No No No No SL No No No No No No No No No No SL No No SL No SL No SL No No No No No SL No No No No No No SL No No No SL No SL No SL No SL No No SL No SL No SL No SL No No SL No SL No SL No No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 1.22E‐04 No SL 2.16E‐03 3.85E‐03 1.23E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 No SL No SL No SL 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 3.26E‐01 5.12E‐02 No SL 3.15E‐01 9.67E‐01 No SL No SL No SL No SL 9.67E‐01 No SL No SL No SL No SL 3.45E‐03 No SL No SL No SL 9.67E‐01 No SL No SL 3.75E‐04 3.27E‐03 3.36E‐02 2.90E‐03 2.38E‐03 8.57E‐04 2.28E‐02 1.39E‐01 7.88E‐01 7.88E‐01 No SL No SL 2.86E‐02 4.15E‐03 No SL 2.09E‐04 No SL 1.02E+00 3.53E‐01 4.32E‐01 1.62E‐01 2.47E‐02 1.18E‐02 2.54E‐03 1.64E‐02 1.28E‐02 1.38E‐01 7.83E‐03 3.91E‐03 8.18E‐03 2.28E‐01 1.96E‐01 2.21E‐01 1.15E‐02 9.89E‐03 5.06E‐01 1.22E‐02 2.80E‐03 6.90E‐02 1.47E‐03 5.00E‐04 2.27E‐01 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 SCL Basis Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background MRL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 51 5 5 5 5 5 5 5 5 5 0.42 2.2 0.01 290 290 570 290 570 290 290 290 290 290 290 380 290 1900 1900 290 290 290 1.8 1.8 37 18 93 12 18 25 2600 2600 2 5 1 4.4 1 5 5 0.51 1.8 1.8 1.8 0.86 0.86 1 18 0.86 1.8 1.8 0.86 1.8 1.8 1.8 1.9 0.86 0.86 0.86 1.8 7 34 5 5 5 20 20 20 20 20 20 1.8 1.8 1.8 1.8 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg pH Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 2 1 1 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 20 1 1 1 1 1 1 1 2 1 0.15 1.3 0.01 95 95 190 95 190 95 95 190 240 140 190 240 95 1400 1400 120 95 150 0.85 0.77 12 6.4 45 4.1 9.3 9.3 780 770 0.1 1 0.4 1.8 0.4 0.1 1.6 0.18 0.34 0.34 0.34 0.34 0.18 0.31 4.2 0.19 0.34 0.34 0.23 0.34 0.34 0.34 0.34 0.18 0.31 0.2 0.34 1.8 11 1 1 2 6.6 6.6 6.6 6.6 6.6 6.6 0.73 0.73 0.73 0.73 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg pH Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y N N N N N N N N N N N N N Y N N N N N N N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S002 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:35 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals VOCs VOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 7199 8315A 8260B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Hexavalent Chromium Formaldehyde Xylenes, Total 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Page 64 of 108 CAS Number 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 18540299 50000 1330207 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 Result  Value 1.8 1.8 0.74 0.77 1.4 0.82 1.8 1.5 1.8 1.4 1.8 1.8 1.8 0.79 1.4 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 11 11 22 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 5 5 5 5 5 5 5 5 5 5 5 5 5 55 5 5 5 5 5 5 5 5 5 0.29 2.2 5 5 5 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0018 0.0018 0.00074 0.00077 0.0014 0.00082 0.0018 0.0015 0.0018 0.0014 0.0018 0.0018 0.0018 0.00079 0.0014 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.011 0.011 0.011 0.022 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.011 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.055 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.45 2.2 0.005 0.005 0.005 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N Y Y Y Y N Y N Y N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U J J J J U J U J U U U J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note L L, L B L F F Boeing Soil Char Level  (mg/kg) 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 7.28 22.3 41 ‐‐ 2.31 1.3 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 ‐‐ ‐‐ ‐‐ 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 1.29 43 3.4 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No SL No No No No SL No No No No No No No No No No SL No No SL No SL No SL No No No No No SL No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 5.45E‐03 8.18E‐04 1.91E‐03 1.99E‐02 3.62E‐03 1.11E‐04 4.65E‐03 1.25E‐03 1.59E‐02 2.59E‐05 2.02E‐03 4.65E‐03 1.23E‐04 6.08E‐04 1.17E‐03 1.74E‐03 2.03E‐06 1.74E‐02 2.27E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 1.10E+00 4.78E‐04 2.44E‐03 4.78E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 6.87E‐04 2.24E‐04 1.22E‐04 No SL 2.16E‐03 3.85E‐03 1.35E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 No SL No SL No SL 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 3.49E‐01 5.12E‐02 1.47E‐03 5.00E‐04 2.27E‐01 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 11 11 22 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 5 5 5 5 5 5 5 5 5 5 5 5 5 55 5 5 5 5 5 5 5 5 5 0.45 2.2 5 5 5 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 0.37 0.37 0.73 0.73 0.73 0.73 0.73 0.37 0.73 0.73 0.73 0.73 0.73 0.73 0.73 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 8 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 2 1 1 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 22 1 1 1 1 1 1 1 2 1 0.16 1.3 1 1 2 6.6 6.6 6.6 6.6 6.6 6.6 0.73 0.73 0.73 0.73 0.37 0.37 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A Analyte Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Page 65 of 108 CAS Number 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 Result  Value 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 20 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 51 5 5 5 5 5 5 5 5 5 320 320 640 320 640 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.9 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.01 0.01 0.02 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.01 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.051 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.32 0.32 0.64 0.32 0.64 0.32 0.32 0.32 0.32 0.32 0.32 0.42 0.32 2.1 2.1 0.32 0.32 0.32 0.0019 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note L L, L Boeing Soil Char Level  (mg/kg) 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 7.28 22.3 41 ‐‐ 2.31 1.3 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 ‐‐ ‐‐ ‐‐ 1.1 0.416 59 85.3 ‐‐ 0.797 170 0.0204 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL No No No No No No No SL No No No No No No SL No No No SL No No SL No No No No SL No No No No SL No No No No No No No No No No SL No No SL No SL No SL No No No No No SL No No No No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No Ratio Boeing Soil Char Level 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 1.50E‐03 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 1.74E‐03 2.03E‐06 1.74E‐02 2.27E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 1.00E+00 4.35E‐04 2.22E‐03 4.35E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL 6.82E‐03 1.56E‐03 No SL 5.42E‐04 No SL 6.87E‐04 2.24E‐04 1.22E‐04 No SL 2.16E‐03 3.85E‐03 1.23E‐06 No SL 1.68E‐03 1.52E‐03 8.20E‐05 6.85E‐05 3.13E‐04 1.47E‐03 3.13E‐04 1.35E‐03 5.10E‐03 No SL 2.38E‐05 No SL No SL No SL 4.55E‐03 1.20E‐02 8.47E‐05 5.86E‐05 No SL 6.27E‐03 2.94E‐05 2.45E‐01 3.48E‐01 1.07E+00 No SL No SL No SL No SL 1.07E+00 No SL No SL No SL No SL 3.82E‐03 No SL No SL No SL 1.07E+00 No SL No SL 3.96E‐04 SCL Basis Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 20 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 51 5 5 5 5 5 5 5 5 5 320 320 640 320 640 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 0.73 0.73 0.73 0.73 0.73 0.37 0.73 0.73 0.73 0.73 0.73 0.73 0.73 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 7 0.5 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 2 1 1 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 20 1 1 1 1 1 1 1 2 1 110 110 210 110 210 110 110 210 270 160 210 270 110 1600 1600 130 110 160 0.9 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2008 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2008S003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/18/13 11:45 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Analysis  Method 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 7199 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A Analyte Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Hexavalent Chromium 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene Page 66 of 108 CAS Number 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 18540299 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 Result  Value 1.9 40 19 99 13 19 26 2800 2800 0.11 2.3 0.98 1.9 0.44 0.11 4.3 0.19 1.9 1.9 1.9 1.9 0.93 0.93 1.1 19 0.93 1.9 1.9 0.93 1.9 1.9 1.9 2 0.93 0.93 0.93 1.9 7.5 37 2.2 0.0251 0.0251 0.104 5.6 5.6 5.6 5.6 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.1 1.1 1.9 0.81 0.91 2.2 1.8 1.8 1.8 1.8 1.8 1.3 1.7 0.911 6.65 0.0724 0.0832 0.0831 0.0736 0.233 0.0577 0.181 0.0673 0.0886 0.0571 0.0956 0.0244 0.0282 2.88 19.3 1.31 2.34 3.34 90.1 0.435 0.346 0.145 0.123 330 330 670 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.0019 mg/kg 0.04 mg/kg 0.019 mg/kg 0.099 mg/kg 0.013 mg/kg 0.019 mg/kg 0.026 mg/kg 2.8 mg/kg 2.8 mg/kg 2.2 mg/kg 2.3 mg/kg 1.1 mg/kg 4.9 mg/kg 1.1 mg/kg 5.5 mg/kg 5.5 mg/kg 0.54 mg/kg 1.9 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00093 mg/kg 0.00093 mg/kg 0.0011 mg/kg 0.019 mg/kg 0.00093 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00093 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.002 mg/kg 0.00093 mg/kg 0.00093 mg/kg 0.00093 mg/kg 0.0019 mg/kg 0.0075 mg/kg 0.037 mg/kg 2.2 mg/kg 2.51E‐08 mg/kg 2.51E‐08 mg/kg 0.000000104 mg/kg 5.6 mg/kg 5.6 mg/kg 5.6 mg/kg 5.6 mg/kg 11 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0011 mg/kg 0.0011 mg/kg 0.0019 mg/kg 0.00081 mg/kg 0.00091 mg/kg 0.0022 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0013 mg/kg 0.0017 mg/kg 0.000000911 mg/kg 0.00000665 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000111 mg/kg 0.00000111 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000334 mg/kg 0.0000901 mg/kg 0.00000555 mg/kg 0.00000555 mg/kg 0.00000111 mg/kg 0.00000111 mg/kg 0.33 mg/kg 0.33 mg/kg 0.67 mg/kg Detected N N N N N N N N N N Y N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N Y Y Y N N N N N N N N N N N N N N N N N Y Y Y Y Y Y N Y N N N Y Y Y Y N N N N N N N N N N N N N N N N N Y Y N N N N N N N Project  Qual  Code U U U U U U UJ U U U J U U U UJ U U Validation Note L L L F Q F B U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J J F, F F F, F F J J U J U U U J J J U UJ UJ U UJ UJ U U UJ UJ UJ U U UJ UJ UJ UJ J UJ UJ UJ UJ U U U F, F, B F, F, B F, F, B M, F, F, B M, F, F, B F, F, B M, F M, F, F, B F, F, B F, F, B M, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B F, F, B F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.55 No 3.45E‐03 Ecological RBSL 1.1 No 3.64E‐02 Ecological RBSL 6.2 No 3.06E‐03 Ecological RBSL 39 No 2.54E‐03 Ecological RBSL 14 No 9.29E‐04 Ecological RBSL 0.79 No 2.41E‐02 Ecological RBSL 0.18 No 1.44E‐01 Ecological RBSL 3.3 No 8.48E‐01 MRL 3.3 No 8.48E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 3.14E‐02 Ecological RBSL 2340 No 2.09E‐03 Ecological RBSL ‐‐ No SL No SL 863.2 No 6.37E‐03 Background ‐‐ No SL No SL 0.5 Yes 1.08E+00 MRL 1.29 Yes 1.47E+00 Suburban Residential RBSL 0.0051 No 3.73E‐01 Ecological RBSL 0.004164 No 4.56E‐01 Background 0.006101 No 3.11E‐01 Background 0.0348 No 2.67E‐02 Suburban Residential RBSL 0.073 No 1.27E‐02 Ecological RBSL 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.73E‐02 Ecological RBSL 0.067 No 1.39E‐02 Ecological RBSL 0.013 No 1.46E‐01 Ecological RBSL 0.23 No 8.26E‐03 Ecological RBSL 0.22 No 4.23E‐03 Ecological RBSL 0.22 No 8.64E‐03 Ecological RBSL 0.0079 No 2.41E‐01 Ecological RBSL 0.0092 No 2.07E‐01 Ecological RBSL 0.0086 No 2.33E‐01 Ecological RBSL 0.075 No 1.24E‐02 Ecological RBSL 0.087 No 1.07E‐02 Ecological RBSL 0.0017 No 5.47E‐01 MRL 0.0328 No 5.79E‐02 Suburban Residential RBSL 2.5 No 3.00E‐03 Ecological RBSL 0.493 No 7.51E‐02 Suburban Residential RBSL 43 No 5.12E‐02 Ecological RBSL 0.0000057 No 4.40E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 1.85E‐01 Background 1400 No 4.00E‐03 1400 No 4.00E‐03 1400 No 4.00E‐03 1 Yes 5.60E+00 1400 No 7.86E‐03 0.32 No 6.25E‐02 Ecological RBSL 90 No 2.22E‐04 Ecological RBSL 2.3 No 8.70E‐03 Ecological RBSL 4.5 No 4.44E‐03 Ecological RBSL 0.11 No 1.82E‐01 Ecological RBSL 13 No 1.54E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 5.45E‐03 Ecological RBSL 2.2 No 8.18E‐04 Ecological RBSL 0.387 No 2.84E‐03 Suburban Residential RBSL 0.0387 No 2.84E‐02 Suburban Residential RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 7.4 No 1.09E‐04 Ecological RBSL 0.387 No 2.35E‐03 Suburban Residential RBSL 1.2 No 1.83E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 3.33E‐05 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 14.6 No 1.23E‐04 Suburban Residential RBSL 1.3 No 1.00E‐03 Ecological RBSL 1.2 No 1.42E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.59E‐01 Ecological RBSL 0.3 Yes 1.10E+00 MRL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 1.9 40 19 99 13 19 26 2800 2800 2.2 5.5 1.1 4.9 1.1 5.5 5.5 0.54 0.44 1.9 1.9 1.9 0.93 0.93 1.1 19 0.93 1.9 1.9 0.93 1.9 1.9 1.9 2 0.93 0.93 0.93 1.9 7.5 37 2.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.83 13 6.8 48 4.4 9.9 9.9 840 830 0.11 1.1 0.44 1.9 0.44 0.11 1.8 0.19 0.15 0.37 0.37 0.37 0.37 0.19 0.33 4.5 0.2 0.37 0.37 0.25 0.37 0.37 0.37 0.37 0.19 0.33 0.21 0.37 1.9 12 1.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 5.6 5.6 5.6 5.6 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5.55 5.55 5.55 5.55 5.55 5.55 5.55 5.55 5.55 5.55 5.55 5.55 5.55 1.11 1.11 5.55 5.55 5.55 5.55 11.1 11.1 5.55 5.55 1.11 1.11 330 330 670 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg 2.2 2.2 2.2 2.2 4.5 6.6 6.6 6.6 6.6 6.6 6.6 0.73 0.73 0.73 0.73 0.37 0.37 0.73 0.73 0.73 0.73 0.73 0.37 0.73 0.73 0.73 0.73 0.73 0.73 0.73 0.0183 0.047 0.0233 0.019 0.0356 0.0188 0.0369 0.0206 0.0376 0.0192 0.0345 0.0188 0.0177 0.0244 0.0282 0.0205 0.047 0.0192 0.0367 0.0279 0.033 0.0184 0.0345 0.0244 0.0282 110 110 220 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N Y Y N Y N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N Y N N N Y N Y N Y N Y N Y N N Y Y N Y N Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009D003 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 14:10 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7199 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Hexavalent Chromium Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran Page 67 of 108 CAS Number 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 18540299 7439976 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 Result  Value 330 670 330 330 330 330 330 330 450 330 2200 2200 330 330 330 1.9 1.9 40 19 100 13 19 27 2800 2800 0.11 3 3.4 2.2 0.45 0.11 12.3 4.5 0.19 21100 87.5 0.83 3.21 25.9 5.02 31.3 227 1640 326 43.6 53.9 4.24 0.127 7.07 0.0577 12 5.94 0.184 15.5 0.109 0.0418 0.242 0.28 0.0144 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.93 0.93 1.1 19 0.93 1.9 1.9 0.93 1.9 1.9 1.9 2 0.93 0.93 0.93 1.9 7.5 37 2.2 3.21 3.52 7.06 80.9 260 7.94 2.14 1.46 0.83 7.12 0.155 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.33 mg/kg 0.67 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.45 mg/kg 0.33 mg/kg 2.2 mg/kg 2.2 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.04 mg/kg 0.019 mg/kg 0.1 mg/kg 0.013 mg/kg 0.019 mg/kg 0.027 mg/kg 2.8 mg/kg 2.8 mg/kg 2.2 mg/kg 3 mg/kg 3.4 mg/kg 2.2 mg/kg 1.1 mg/kg 5.6 mg/kg 12.3 mg/kg 0.0045 mg/kg 0.53 mg/kg 21100 mg/kg 87.5 mg/kg 0.83 mg/kg 3.21 mg/kg 25.9 mg/kg 5.02 mg/kg 31.3 mg/kg 227 mg/kg 1640 mg/kg 326 mg/kg 43.6 mg/kg 53.9 mg/kg 4.24 mg/kg 0.219 mg/kg 7.07 mg/kg 0.0577 mg/kg 12 mg/kg 5.94 mg/kg 0.184 mg/kg 15.5 mg/kg 0.438 mg/kg 0.0418 mg/kg 0.242 mg/kg 0.28 mg/kg 0.0144 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00093 mg/kg 0.00093 mg/kg 0.0011 mg/kg 0.019 mg/kg 0.00093 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00093 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.002 mg/kg 0.00093 mg/kg 0.00093 mg/kg 0.00093 mg/kg 0.0019 mg/kg 0.0075 mg/kg 0.037 mg/kg 2.2 mg/kg 0.00000321 mg/kg 0.00000352 mg/kg 0.00000706 mg/kg 0.0000809 mg/kg 0.00026 mg/kg 0.00000794 mg/kg 0.00000214 mg/kg 0.00000146 mg/kg 0.00000083 mg/kg 0.00000712 mg/kg 0.00000509 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y N Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U UJ U U U J J J U UJ U U Validation Note L L Q Q Q F, B B J F J U B J U J J J U U U U U U U U U UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ U J J J UJ S S S S S S S S S S S S S S S S S S S S S F, F, B F, F, B F, F, B F, F, B F, F, B F, F, B F M, F, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.10E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL 110 No 4.09E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.10E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.96E‐04 Ecological RBSL 0.55 No 3.45E‐03 Ecological RBSL 1.1 No 3.64E‐02 Ecological RBSL 6.2 No 3.06E‐03 Ecological RBSL 39 No 2.56E‐03 Ecological RBSL 14 No 9.29E‐04 Ecological RBSL 0.79 No 2.41E‐02 Ecological RBSL 0.18 No 1.50E‐01 Ecological RBSL 3.3 No 8.48E‐01 MRL 3.3 No 8.48E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 9.71E‐02 Ecological RBSL 2340 No 9.40E‐04 Ecological RBSL ‐‐ No SL No SL 863.2 No 6.49E‐03 Background ‐‐ No SL No SL 0.5 No 9.00E‐03 Ecological RBSL 0.5 Yes 1.06E+00 MRL 37900 No 5.57E‐01 Background 203.8 No 4.29E‐01 Background 4.8 No 1.73E‐01 Ecological RBSL 22 No 1.46E‐01 Ecological RBSL 60.11 No 4.31E‐01 Background 26.18 No 1.92E‐01 Background 64.4 No 4.86E‐01 Background 723 No 3.14E‐01 Background 7524 No 2.18E‐01 Background 754 No 4.32E‐01 Background 111.8 No 3.90E‐01 Background 153 No 3.52E‐01 Background 10.64 No 3.98E‐01 Background 0.5 No 4.38E‐01 MRL 24.2 No 2.92E‐01 Background 0.435 No 1.33E‐01 Background 42 No 2.86E‐01 Background 33.9 No 1.75E‐01 Background 1.642 No 1.12E‐01 Background 64.2 No 2.41E‐01 Background 1 No 4.38E‐01 MRL 0.99 No 4.22E‐02 Ecological RBSL 0.761 No 3.18E‐01 Suburban Residential RBSL 1.29 No 2.17E‐01 Suburban Residential RBSL 0.87 No 1.66E‐02 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.58E‐01 Ecological RBSL 0.18 No 1.06E‐01 Ecological RBSL 0.082 No 2.32E‐01 Ecological RBSL 0.043 No 4.42E‐01 Ecological RBSL 0.017 Yes 1.12E+00 MRL 0.039 No 4.87E‐01 Ecological RBSL 0.025 No 7.60E‐01 Ecological RBSL 0.0051 No 3.73E‐01 Ecological RBSL 0.004164 No 4.56E‐01 Background 0.006101 No 3.11E‐01 Background 0.0348 No 2.67E‐02 Suburban Residential RBSL 0.073 No 1.27E‐02 Ecological RBSL 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.73E‐02 Ecological RBSL 0.067 No 1.39E‐02 Ecological RBSL 0.013 No 1.46E‐01 Ecological RBSL 0.23 No 8.26E‐03 Ecological RBSL 0.22 No 4.23E‐03 Ecological RBSL 0.22 No 8.64E‐03 Ecological RBSL 0.0079 No 2.41E‐01 Ecological RBSL 0.0092 No 2.07E‐01 Ecological RBSL 0.0086 No 2.33E‐01 Ecological RBSL 0.075 No 1.24E‐02 Ecological RBSL 0.087 No 1.07E‐02 Ecological RBSL 0.0017 No 5.47E‐01 MRL 0.0328 No 5.79E‐02 Suburban Residential RBSL 2.5 No 3.00E‐03 Ecological RBSL 0.493 No 7.51E‐02 Suburban Residential RBSL 43 No 5.12E‐02 Ecological RBSL 0.0000057 No 5.63E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.25E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 330 670 330 330 330 330 330 330 450 330 2200 2200 330 330 330 1.9 1.9 40 19 100 13 19 27 2800 2800 2.2 5.6 1.1 4.9 1.1 5.6 5.6 4.5 0.53 10.9 0.547 0.274 5.47 0.821 0.547 2.2 0.547 54.7 54.7 0.547 2.19 5.47 0.219 0.438 0.109 0.219 0.219 0.109 0.438 0.438 0.109 0.109 0.45 0.103 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.93 0.93 1.1 19 0.93 1.9 1.9 0.93 1.9 1.9 1.9 2 0.93 0.93 0.93 1.9 7.5 37 2.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 110 220 110 110 220 280 170 220 280 110 1700 1700 140 110 170 0.91 0.83 13 6.9 49 4.4 10 10 840 830 0.11 1.1 0.45 2 0.45 0.11 1.8 2.3 0.19 8.44 0.0361 0.0733 0.908 0.0963 0.0985 0.6 0.0908 14.8 18.3 0.12 0.219 0.908 0.0744 0.0919 0.0503 0.16 0.016 0.0569 0.169 0.109 0.0219 0.0328 0.16 0.0103 3.6 3.6 4 5.1 8.8 3.6 3.6 3.6 5.4 0.37 0.37 0.37 0.37 0.19 0.33 4.5 0.2 0.37 0.37 0.25 0.37 0.37 0.37 0.37 0.19 0.33 0.21 0.37 1.9 12 1.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 5.09 5.09 5.09 5.09 5.09 5.09 5.09 5.09 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0547 0.162 0.0701 0.0525 0.0633 0.0514 0.0694 0.0538 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N N Y N N N N N Y Y N N N N Y Y N N Y N Y Y N Y N Y Y Y N N Y N Y Y Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A Analyte 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone Page 68 of 108 CAS Number 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 Result  Value 3.82 0.297 0.689 1.03 0.163 0.0779 0.0496 352 521 52.4 36.2 642 3320 4.56 2.83 1.87 0.295 320 320 630 320 630 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.8 1.8 38 32 95 13 18 25 2600 2600 0.11 7.8 3.1 5.3 0.42 0.23 26.7 0.19 20800 108 0.774 3.82 22.9 6.17 22.7 294 2210 169 42.6 73.9 4.38 0.257 9.64 0.146 25.6 11.3 0.624 14.7 0.157 0.0427 0.246 0.0147 18 18 18 18 18 18 18 18 18 4.5 2 1.1 0.88 0.88 1.1 72 0.88 1.8 1.8 0.55 1.8 1.8 1.8 1.9 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00000382 mg/kg 0.00000509 mg/kg 0.000000689 mg/kg 0.00000103 mg/kg 0.00000509 mg/kg 0.00000102 mg/kg 4.96E‐08 mg/kg 0.00000509 mg/kg 0.000521 mg/kg 0.00000509 mg/kg 0.00000509 mg/kg 0.000642 mg/kg 0.00332 mg/kg 0.00000509 mg/kg 0.00000509 mg/kg 0.00000102 mg/kg 0.00000102 mg/kg 0.32 mg/kg 0.32 mg/kg 0.63 mg/kg 0.32 mg/kg 0.63 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.42 mg/kg 0.32 mg/kg 2.1 mg/kg 2.1 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.038 mg/kg 0.032 mg/kg 0.095 mg/kg 0.013 mg/kg 0.018 mg/kg 0.025 mg/kg 2.6 mg/kg 2.6 mg/kg 2.1 mg/kg 7.8 mg/kg 3.1 mg/kg 5.3 mg/kg 1.1 mg/kg 0.23 mg/kg 26.7 mg/kg 0.52 mg/kg 20800 mg/kg 108 mg/kg 0.774 mg/kg 3.82 mg/kg 22.9 mg/kg 6.17 mg/kg 22.7 mg/kg 294 mg/kg 2210 mg/kg 169 mg/kg 42.6 mg/kg 73.9 mg/kg 4.38 mg/kg 0.257 mg/kg 9.64 mg/kg 0.146 mg/kg 25.6 mg/kg 11.3 mg/kg 0.624 mg/kg 14.7 mg/kg 0.157 mg/kg 0.0427 mg/kg 0.246 mg/kg 0.0147 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0045 mg/kg 0.002 mg/kg 0.0011 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.0011 mg/kg 0.072 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00055 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg Detected Y N Y Y N N Y N Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N Y Y N N N N N N N Y N N N N Project  Qual  Code J UJ J J UJ UJ J UJ UJ UJ UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U J J U J Validation Note F, F, B M, F, F, B F, B F, F, B M, B, F, F M M, F, F, B F, F, B M, F, F, B M, F, F, B F, F, B F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B L L Q Q Q F, B U J F J J J J U U U U U U U U U U J U U U U U U U J U U U U Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.87 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL Yes No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.48E‐01 1.07E+00 No SL No SL No SL No SL 1.07E+00 No SL No SL No SL No SL 3.82E‐03 No SL No SL No SL 1.07E+00 No SL No SL 3.75E‐04 3.27E‐03 3.45E‐02 5.16E‐03 2.44E‐03 9.29E‐04 2.28E‐02 1.39E‐01 7.88E‐01 7.88E‐01 No SL No SL 8.86E‐02 2.26E‐03 No SL 2.66E‐04 No SL 1.04E+00 5.49E‐01 5.30E‐01 1.61E‐01 1.74E‐01 3.81E‐01 2.36E‐01 3.52E‐01 4.07E‐01 2.94E‐01 2.24E‐01 3.81E‐01 4.83E‐01 4.12E‐01 5.14E‐01 3.98E‐01 3.36E‐01 6.10E‐01 3.33E‐01 3.80E‐01 2.29E‐01 1.57E‐01 4.31E‐02 3.23E‐01 1.69E‐02 No SL No SL 1.50E‐01 1.00E‐01 2.20E‐01 4.19E‐01 1.06E+00 4.62E‐01 7.20E‐01 8.82E‐01 4.80E‐01 1.80E‐01 2.53E‐02 1.21E‐02 2.79E‐03 6.55E‐02 1.31E‐02 1.38E‐01 7.83E‐03 2.50E‐03 8.18E‐03 2.28E‐01 1.96E‐01 2.21E‐01 SCL Basis Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.09 5.09 5.09 5.09 5.09 1.02 1.02 5.09 5.09 5.09 5.09 10.2 10.2 5.09 5.09 1.02 1.02 320 320 630 320 630 320 320 320 320 320 320 420 320 2100 2100 320 320 320 1.8 1.8 38 18 95 13 18 25 2600 2600 2.1 5.3 1.1 4.9 1.1 5.3 5.3 0.52 10.2 0.512 0.256 5.12 0.768 0.512 2 0.512 51.2 51.2 0.512 2.05 5.12 0.205 0.41 0.102 0.205 0.205 0.102 0.41 0.41 0.102 0.102 0.0994 18 18 18 18 18 18 18 18 18 4.5 1.8 1.8 0.88 0.88 1.1 72 0.88 1.8 1.8 0.88 1.8 1.8 1.8 1.9 RL Units MDL ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0671 0.0377 0.05 0.0485 0.0329 0.0457 0.0359 0.0615 0.162 0.0515 0.0666 0.0486 0.08 0.0351 0.05 0.0457 0.0359 110 110 210 110 210 110 110 210 260 160 210 260 110 1600 1600 130 110 160 0.86 0.79 13 6.5 46 4.2 9.5 9.5 800 790 0.11 1.1 0.42 1.9 0.42 0.11 1.7 0.19 7.9 0.0338 0.0686 0.85 0.0901 0.0922 0.56 0.085 13.8 17.1 0.113 0.205 0.85 0.0696 0.086 0.0471 0.15 0.015 0.0533 0.158 0.102 0.0205 0.0307 0.0099 3.4 3.4 3.8 4.8 8.4 3.4 18 18 5.1 4.5 0.35 0.35 0.35 0.18 0.32 72 0.19 0.47 0.35 0.23 0.35 0.35 0.35 0.35 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S001 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S002 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:40 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 13:50 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Analysis  Method 8081A 8081A 8081A 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 7199 8315A 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A Analyte gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene Page 69 of 108 CAS Number 58899 76448 1024573 2385855 72435 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 Result  Value 0.88 0.88 0.47 1.8 7.1 35 5.5 4.8 2.4 5.5 9.4 20 20 20 20 20 20 1.8 1.8 1.8 1.8 0.48 0.9 1.2 1.2 2.5 1.8 0.97 2.4 1.8 3.9 1.8 1.2 1.8 1.7 7.3 4.4 0.85 2.2 0.031 0.031 0.133 5.7 5.7 3.1 5.7 6.7 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 0.96 1.9 1.9 0.95 1.9 1.4 1.9 1.9 1.9 0.78 1.4 1.23 6.91 0.0962 0.0965 0.0722 0.0481 0.225 0.0507 0.167 0.0484 0.0389 0.0926 0.0325 0.0293 0.0282 4.2 18.1 1.45 1.83 5.77 89.9 0.491 0.342 0.183 0.103 340 340 680 340 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00088 mg/kg 0.00088 mg/kg 0.00047 mg/kg 0.0018 mg/kg 0.0071 mg/kg 0.035 mg/kg 5.5 mg/kg 4.8 mg/kg 2.4 mg/kg 5.5 mg/kg 9.4 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00048 mg/kg 0.0009 mg/kg 0.0012 mg/kg 0.0012 mg/kg 0.0025 mg/kg 0.0018 mg/kg 0.00097 mg/kg 0.0024 mg/kg 0.0018 mg/kg 0.0039 mg/kg 0.0018 mg/kg 0.0012 mg/kg 0.0018 mg/kg 0.0017 mg/kg 0.0073 mg/kg 0.0044 mg/kg 0.85 mg/kg 2.2 mg/kg 0.000000031 mg/kg 0.000000031 mg/kg 0.000000133 mg/kg 5.7 mg/kg 5.7 mg/kg 3.1 mg/kg 5.7 mg/kg 6.7 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00096 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00095 mg/kg 0.0019 mg/kg 0.0014 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00078 mg/kg 0.0014 mg/kg 0.00000123 mg/kg 0.00000691 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.000000225 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000113 mg/kg 0.00000113 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000577 mg/kg 0.0000899 mg/kg 0.00000566 mg/kg 0.00000566 mg/kg 0.00000113 mg/kg 0.00000113 mg/kg 0.34 mg/kg 0.34 mg/kg 0.68 mg/kg 0.34 mg/kg Detected N N Y N N N N Y Y N Y N N N N N N N N N N Y Y Y Y Y Y Y Y N Y N Y N Y Y N Y N Y Y Y N N Y N Y N N N N N N N N N N N N N N Y N N Y N Y N N N Y Y Y Y N N N N Y N N N N N N N N N N N N Y Y N N N N N N N N Project  Qual  Code U U J U U U U J J U J U U U U U U U U U U J J J J Validation Note F, F F F, F F J J U U J U J U B U U U J U J U U U U U U U U U U U U U U J U U J U J U U U J J J UJ UJ UJ UJ J U U UJ U UJ UJ U U UJ UJ UJ UJ J UJ UJ UJ UJ U U U U F, F F F, F F F, F, B F, F, B M, B, F, F M, F, F, B M, F, F, B M, F, F, B F F, F, B F, F, B M, F, F, B F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B F, F, B F, F, B M, F, F, B M, F, F, B M, F, F, B M, F, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.075 No 1.17E‐02 Ecological RBSL 0.087 No 1.01E‐02 Ecological RBSL 0.0017 No 2.76E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.84E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 1400 No 3.93E‐03 1400 No 3.43E‐03 1400 No 1.71E‐03 1 Yes 5.50E+00 1400 No 6.71E‐03 0.32 No 6.25E‐02 Ecological RBSL 90 No 2.22E‐04 Ecological RBSL 2.3 No 8.70E‐03 Ecological RBSL 4.5 No 4.44E‐03 Ecological RBSL 0.11 No 1.82E‐01 Ecological RBSL 13 No 1.54E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 1.45E‐03 Ecological RBSL 2.2 No 4.09E‐04 Ecological RBSL 0.387 No 3.10E‐03 Suburban Residential RBSL 0.0387 No 3.10E‐02 Suburban Residential RBSL 0.387 No 6.46E‐03 Suburban Residential RBSL 7.4 No 2.43E‐04 Ecological RBSL 0.387 No 2.51E‐03 Suburban Residential RBSL 1.2 No 2.00E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 7.22E‐05 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 3.10E‐03 Suburban Residential RBSL 14.6 No 1.23E‐04 Suburban Residential RBSL 1.3 No 1.31E‐03 Ecological RBSL 1.2 No 6.08E‐03 Ecological RBSL 0.5 No 8.80E‐03 Ecological RBSL 1.29 No 6.59E‐01 Suburban Residential RBSL 43 No 5.12E‐02 Ecological RBSL 0.0000057 No 5.44E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 2.36E‐01 Background 1400 No 4.07E‐03 1400 No 4.07E‐03 1400 No 2.21E‐03 1 Yes 5.70E+00 1400 No 4.79E‐03 0.32 No 6.25E‐02 Ecological RBSL 90 No 2.22E‐04 Ecological RBSL 2.3 No 8.70E‐03 Ecological RBSL 4.5 No 4.44E‐03 Ecological RBSL 0.11 No 1.82E‐01 Ecological RBSL 13 No 1.54E‐03 Ecological RBSL 0.0325 No 5.85E‐02 Suburban Residential RBSL 7.29 No 2.61E‐04 Suburban Residential RBSL 53 No 3.58E‐05 Ecological RBSL 1.1 No 1.73E‐03 Ecological RBSL 0.33 No 5.76E‐03 Ecological RBSL 2.2 No 8.64E‐04 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 0.0387 No 4.91E‐02 Suburban Residential RBSL 0.387 No 2.48E‐03 Suburban Residential RBSL 7.4 No 2.57E‐04 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 1.2 No 7.92E‐04 Ecological RBSL 0.113 No 1.68E‐02 Suburban Residential RBSL 54 No 2.59E‐05 Ecological RBSL 0.89 No 2.13E‐03 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 14.6 No 1.30E‐04 Suburban Residential RBSL 1.3 No 6.00E‐04 Ecological RBSL 1.2 No 1.17E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.70E‐01 Ecological RBSL 0.3 Yes 1.13E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 0.88 0.88 0.88 1.8 7.1 35 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.4 0.44 2.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 0.18 0.32 0.2 0.35 1.8 12 2.2 2.2 2.2 2.2 4.4 6.5 6.5 6.5 6.5 6.5 6.5 0.72 0.72 0.72 0.72 0.36 0.36 0.72 0.72 0.72 0.72 0.72 0.36 0.72 0.72 0.72 0.72 0.72 0.72 0.72 2.3 0.15 1.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 5.7 5.7 5.7 5.7 11 20 20 20 20 20 20 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 1.9 5.66 5.66 5.66 5.66 5.66 5.66 5.66 5.66 5.66 5.66 5.66 5.66 5.66 1.13 1.13 5.66 5.66 5.66 5.66 11.3 11.3 5.66 5.66 1.13 1.13 340 340 680 340 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg 2.3 2.3 2.3 2.3 4.6 6.8 6.8 6.8 6.8 6.8 6.8 0.75 0.75 0.75 0.75 0.38 0.38 0.75 0.75 0.75 0.75 0.75 0.38 0.75 0.75 0.75 0.75 0.75 0.75 0.75 0.0199 0.0532 0.0261 0.0205 0.0381 0.0205 0.0404 0.0217 0.0373 0.0237 0.0389 0.0205 0.022 0.0293 0.0282 0.0226 0.0532 0.0208 0.0386 0.0321 0.038 0.0228 0.0389 0.0293 0.0282 110 110 230 110 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N Y Y N N Y N Y Y Y N Y N Y N Y N Y N Y Y N N Y N Y N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2009S003 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/12/13 14:00 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7199 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 9045C 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Hexavalent Chromium Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal pH 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran Page 70 of 108 CAS Number 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 18540299 7439976 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal E‐10139 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 Result  Value 680 340 340 340 340 340 340 460 340 2300 2300 340 340 340 1.9 1.9 41 19 100 14 19 27 2800 2800 0.11 2.2 3.2 2.2 0.45 0.21 13.9 4.6 0.2 21400 91 0.777 3.3 25.6 4.69 31.8 199 1830 313 38.2 52.1 4.36 0.12 6.2 0.0646 10.4 5 0.179 16.1 0.111 0.0504 0.274 1.7 0.0144 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.95 0.95 1.1 19 0.95 1.9 1.9 0.95 1.9 1.9 1.9 2.1 0.95 0.95 0.95 1.9 7.6 38 2.3 10.8 12.1 19.5 6.71 85.3 524 4.3 2.9 6.92 6.07 15.7 0.86 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.68 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.46 mg/kg 0.34 mg/kg 2.3 mg/kg 2.3 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.041 mg/kg 0.019 mg/kg 0.1 mg/kg 0.014 mg/kg 0.019 mg/kg 0.027 mg/kg 2.8 mg/kg 2.8 mg/kg 2.3 mg/kg 2.2 mg/kg 3.2 mg/kg 2.2 mg/kg 1.1 mg/kg 0.21 mg/kg 13.9 mg/kg 0.0046 mg/kg 0.56 mg/kg 21400 mg/kg 91 mg/kg 0.777 mg/kg 3.3 mg/kg 25.6 mg/kg 4.69 mg/kg 31.8 mg/kg 199 mg/kg 1830 mg/kg 313 mg/kg 38.2 mg/kg 52.1 mg/kg 4.36 mg/kg 0.222 mg/kg 6.2 mg/kg 0.0646 mg/kg 10.4 mg/kg 5 mg/kg 0.179 mg/kg 16.1 mg/kg 0.443 mg/kg 0.0504 mg/kg 0.274 mg/kg 1.7 mg/kg 0.0144 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00095 mg/kg 0.00095 mg/kg 0.0011 mg/kg 0.019 mg/kg 0.00095 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00095 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0021 mg/kg 0.00095 mg/kg 0.00095 mg/kg 0.00095 mg/kg 0.0019 mg/kg 0.0076 mg/kg 0.038 mg/kg 2.3 mg/kg 0.0000108 mg/kg 0.0000121 mg/kg 0.0000195 mg/kg 6.71 ph Units 0.0000853 mg/kg 0.000524 mg/kg 0.0000043 mg/kg 0.0000029 mg/kg 0.00000692 mg/kg 0.00000607 mg/kg 0.0000157 mg/kg 0.00000086 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U UJ U U U J J J U J U U Validation Note L L Q Q Q F, B B J F J U B J U J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J J F F, B F, B F, B F F, B J F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.13E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 4.18E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.13E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.96E‐04 Ecological RBSL 0.55 No 3.45E‐03 Ecological RBSL 1.1 No 3.73E‐02 Ecological RBSL 6.2 No 3.06E‐03 Ecological RBSL 39 No 2.56E‐03 Ecological RBSL 14 No 1.00E‐03 Ecological RBSL 0.79 No 2.41E‐02 Ecological RBSL 0.18 No 1.50E‐01 Ecological RBSL 3.3 No 8.48E‐01 MRL 3.3 No 8.48E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 9.14E‐02 Ecological RBSL 2340 No 9.40E‐04 Ecological RBSL ‐‐ No SL No SL 863.2 No 2.43E‐04 Background ‐‐ No SL No SL 0.5 No 9.20E‐03 Ecological RBSL 0.5 Yes 1.12E+00 MRL 37900 No 5.65E‐01 Background 203.8 No 4.47E‐01 Background 4.8 No 1.62E‐01 Ecological RBSL 22 No 1.50E‐01 Ecological RBSL 60.11 No 4.26E‐01 Background 26.18 No 1.79E‐01 Background 64.4 No 4.94E‐01 Background 723 No 2.75E‐01 Background 7524 No 2.43E‐01 Background 754 No 4.15E‐01 Background 111.8 No 3.42E‐01 Background 153 No 3.41E‐01 Background 10.64 No 4.10E‐01 Background 0.5 No 4.44E‐01 MRL 24.2 No 2.56E‐01 Background 0.435 No 1.49E‐01 Background 42 No 2.48E‐01 Background 33.9 No 1.47E‐01 Background 1.642 No 1.09E‐01 Background 64.2 No 2.51E‐01 Background 1 No 4.43E‐01 MRL 0.99 No 5.09E‐02 Ecological RBSL 0.761 No 3.60E‐01 Suburban Residential RBSL 1.29 Yes 1.32E+00 Suburban Residential RBSL 0.87 No 1.66E‐02 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.58E‐01 Ecological RBSL 0.18 No 1.06E‐01 Ecological RBSL 0.082 No 2.32E‐01 Ecological RBSL 0.043 No 4.42E‐01 Ecological RBSL 0.017 Yes 1.12E+00 MRL 0.039 No 4.87E‐01 Ecological RBSL 0.025 No 7.60E‐01 Ecological RBSL 0.0051 No 3.73E‐01 Ecological RBSL 0.004164 No 4.56E‐01 Background 0.006101 No 3.11E‐01 Background 0.0348 No 2.73E‐02 Suburban Residential RBSL 0.073 No 1.30E‐02 Ecological RBSL 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.73E‐02 Ecological RBSL 0.067 No 1.42E‐02 Ecological RBSL 0.013 No 1.46E‐01 Ecological RBSL 0.23 No 8.26E‐03 Ecological RBSL 0.22 No 4.32E‐03 Ecological RBSL 0.22 No 8.64E‐03 Ecological RBSL 0.0079 No 2.41E‐01 Ecological RBSL 0.0092 No 2.07E‐01 Ecological RBSL 0.0086 No 2.44E‐01 Ecological RBSL 0.075 No 1.27E‐02 Ecological RBSL 0.087 No 1.09E‐02 Ecological RBSL 0.0017 No 5.59E‐01 MRL 0.0328 No 5.79E‐02 Suburban Residential RBSL 2.5 No 3.04E‐03 Ecological RBSL 0.493 No 7.71E‐02 Suburban Residential RBSL 43 No 5.35E‐02 Ecological RBSL 0.0000057 Yes 1.89E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 3.46E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 680 340 340 340 340 340 340 460 340 2300 2300 340 340 340 1.9 1.9 41 19 100 14 19 27 2800 2800 2.3 5.7 1.1 4.9 1.1 5.7 5.7 4.6 0.56 11.1 0.554 0.277 5.54 0.831 0.554 2.2 0.554 55.4 55.4 0.554 2.22 5.54 0.222 0.443 0.111 0.222 0.222 0.111 0.443 0.443 0.111 0.111 0.46 0.11 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.95 0.95 1.1 19 0.95 1.9 1.9 0.95 1.9 1.9 1.9 2.1 0.95 0.95 0.95 1.9 7.6 38 2.3 0.01 5.59 5.59 5.59 5.59 5.59 5.59 5.59 5.59 MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 230 110 110 230 290 170 230 290 110 1700 1700 140 110 170 0.93 0.85 14 7.1 50 4.6 10 10 860 850 0.11 1.1 0.45 2 0.45 0.11 1.8 2.4 0.2 8.55 0.0366 0.0743 0.92 0.0975 0.0997 0.61 0.092 15 18.5 0.122 0.222 0.92 0.0754 0.0931 0.051 0.162 0.0162 0.0576 0.171 0.111 0.0222 0.0332 0.16 0.011 3.8 3.8 4.1 5.2 9.1 3.8 3.8 3.8 5.6 0.38 0.38 0.38 0.38 0.19 0.34 4.6 0.21 0.38 0.38 0.25 0.38 0.38 0.38 0.38 0.19 0.34 0.22 0.38 1.9 13 1.4 Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Y Y Y 0.01 pH Units Y 0.0504 ng/kg Y 0.229 ng/kg Y 0.0873 ng/kg Y 0.0632 ng/kg Y 0.081 ng/kg Y 0.0551 ng/kg Y 0.0907 ng/kg Y 0.0751 ng/kg Y Y Y Y Y Y Y Y Y Y Y Y Y ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N Y Y N Y Y N Y Y Y Y Y N N Y Y Y Y N N Y Y N Y N N Y N Y N N N Y Y N Y N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A Analyte 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Page 71 of 108 CAS Number 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 Result  Value 17.4 0.911 4.11 4.73 1.08 0.314 0.439 187 1140 125 126 192 12400 38.3 20.7 15.1 2.1 310 310 620 310 620 310 310 310 310 310 310 410 310 2100 2100 310 310 310 1.9 1.9 41 18 100 14 19 27 2800 2800 0.11 16.2 0.6 23 0.45 0.11 14.9 0.2 15500 85.4 0.712 3.26 20.3 5.28 17.2 285 3020 72.7 35.5 43.8 4.25 0.0934 7 0.148 9.3 7.3 0.587 12.3 0.156 0.0368 0.222 19 19 19 19 19 19 19 9.9 19 1.9 0.4 0.53 0.94 0.94 1.1 19 0.94 1.9 1.9 0.94 1.9 1.9 1.9 2 0.94 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.0000174 mg/kg 0.00000559 mg/kg 0.00000411 mg/kg 0.00000473 mg/kg 0.00000559 mg/kg 0.000000314 mg/kg 0.00000112 mg/kg 0.00000559 mg/kg 0.00114 mg/kg 0.00000559 mg/kg 0.00000559 mg/kg 0.000192 mg/kg 0.0124 mg/kg 0.00000559 mg/kg 0.00000559 mg/kg 0.00000112 mg/kg 0.00000112 mg/kg 0.31 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.62 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.41 mg/kg 0.31 mg/kg 2.1 mg/kg 2.1 mg/kg 0.31 mg/kg 0.31 mg/kg 0.31 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.041 mg/kg 0.018 mg/kg 0.1 mg/kg 0.014 mg/kg 0.019 mg/kg 0.027 mg/kg 2.8 mg/kg 2.8 mg/kg 2.2 mg/kg 16.2 mg/kg 0.6 mg/kg 23 mg/kg 1.1 mg/kg 5.6 mg/kg 14.9 mg/kg 0.56 mg/kg 15500 mg/kg 85.4 mg/kg 0.712 mg/kg 5.43 mg/kg 20.3 mg/kg 5.28 mg/kg 17.2 mg/kg 285 mg/kg 3020 mg/kg 72.7 mg/kg 35.5 mg/kg 43.8 mg/kg 4.25 mg/kg 0.217 mg/kg 7 mg/kg 0.148 mg/kg 9.3 mg/kg 7.3 mg/kg 0.587 mg/kg 12.3 mg/kg 0.156 mg/kg 0.0368 mg/kg 0.222 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0099 mg/kg 0.019 mg/kg 0.0019 mg/kg 0.0004 mg/kg 0.00053 mg/kg 0.00094 mg/kg 0.00094 mg/kg 0.0011 mg/kg 0.019 mg/kg 0.00094 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.00094 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.0019 mg/kg 0.002 mg/kg 0.00094 mg/kg Detected Y N Y Y N Y N N Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N Y Y Y N N Y N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N N N N N N Y N N Y Y N N N N N N N N N N N N N Project  Qual  Code UJ J J UJ J UJ UJ UJ UJ UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U J U U U UJ U U U J J J U UJ J U Validation Note B M, F, B F F M, F, B B M M, F, B F, B M, F, B M, F, B B, F F, B M, F, B M, F, B M, F, B M, F, B L Q Q Q Q Q, F Q, Q U B J Q, Q Q J UJ Q, Q Q, Q J J Q, Q, B Q, Q J J J Q, Q U U U U U U U J U U J J U U U U U U U U U U U U U Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 0.075 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL Yes No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.37E‐01 1.03E+00 No SL No SL No SL No SL 1.03E+00 No SL No SL No SL No SL 3.73E‐03 No SL No SL No SL 1.03E+00 No SL No SL 3.96E‐04 3.45E‐03 3.73E‐02 2.90E‐03 2.56E‐03 1.00E‐03 2.41E‐02 1.50E‐01 8.48E‐01 8.48E‐01 No SL No SL 1.71E‐02 9.83E‐03 No SL 6.49E‐03 No SL 1.12E+00 4.09E‐01 4.19E‐01 1.48E‐01 2.47E‐01 3.38E‐01 2.02E‐01 2.67E‐01 3.94E‐01 4.01E‐01 9.64E‐02 3.18E‐01 2.86E‐01 3.99E‐01 4.34E‐01 2.89E‐01 3.40E‐01 2.21E‐01 2.15E‐01 3.57E‐01 1.92E‐01 1.56E‐01 3.72E‐02 2.92E‐01 No SL No SL 1.58E‐01 1.06E‐01 2.32E‐01 4.42E‐01 1.12E+00 2.54E‐01 7.60E‐01 3.73E‐01 9.61E‐02 8.69E‐02 2.70E‐02 1.29E‐02 2.79E‐03 1.73E‐02 1.40E‐02 1.46E‐01 8.26E‐03 4.27E‐03 8.64E‐03 2.41E‐01 2.07E‐01 2.33E‐01 1.25E‐02 SCL Basis Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.59 5.59 5.59 5.59 5.59 1.12 1.12 5.59 5.59 5.59 5.59 11.2 11.2 5.59 5.59 1.12 1.12 310 310 620 310 620 310 310 310 310 310 310 410 310 2100 2100 310 310 310 1.9 1.9 41 19 100 14 19 27 2800 2800 2.2 5.6 1.1 4.9 1.1 5.6 5.6 0.56 10.9 0.543 0.272 5.43 0.815 0.543 2.2 0.543 54.3 54.3 0.543 2.17 5.43 0.217 0.435 0.109 0.217 0.217 0.109 0.435 0.435 0.109 0.109 19 19 19 19 19 19 19 19 19 1.9 1.9 1.9 0.94 0.94 1.1 19 0.94 1.9 1.9 0.94 1.9 1.9 1.9 2 0.94 RL Units MDL ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0852 0.0537 0.133 0.0589 0.0602 0.087 0.0484 0.0638 0.229 0.0623 0.0855 0.0558 0.235 0.0567 0.133 0.087 0.0484 100 100 210 100 210 100 100 210 260 150 210 260 100 1500 1500 130 100 160 0.93 0.85 14 7 50 4.5 10 10 860 850 0.11 1.1 0.45 2 0.45 0.11 1.8 0.2 7.83 0.0359 0.0728 0.913 0.174 0.108 0.37 0.0902 9.06 18.1 0.141 0.217 0.913 0.0934 0.0913 0.05 0.104 0.0174 0.0543 0.0826 0.109 0.0282 0.0326 3.7 3.7 4.1 5.2 9 3.7 3.7 3.7 5.5 0.37 0.37 0.37 0.37 0.19 0.34 4.5 0.2 0.92 0.37 0.25 0.37 0.37 0.37 0.37 0.19 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S001 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:30 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8081A 8081A 8081A 8081A 8081A 8260B 8015B 8015B 8015B 8015B 8015B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Page 72 of 108 CAS Number 76448 1024573 2385855 72435 8001352 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 Result  Value 0.94 0.94 1.9 7.6 37 6 5.3 5.3 5.3 5.3 11 6 6 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 11 11 11 22 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 11 6 6 6 6 6 6 6 6 6 6 6 6 6 55 6 6 6 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.00094 0.00094 0.0019 0.0076 0.037 0.006 5.3 5.3 5.3 5.3 11 0.006 0.006 0.019 0.019 0.019 0.019 0.019 0.019 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.011 0.011 0.011 0.022 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.011 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.006 0.055 0.006 0.006 0.006 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note F Q, L Boeing Soil Char Level  (mg/kg) 0.087 0.0017 0.0328 2.5 0.493 3.4 1400 1400 1400 1 1400 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ 0.733 3.2 ‐‐ 9.22 ‐‐ 7.28 22.3 41 ‐‐ 2.31 1.3 8160 ‐‐ 2.97 3.3 61 73 16 3.4 16 3.7 0.98 ‐‐ 210 ‐‐ ‐‐ ‐‐ 1.1 0.416 Exceeds Boeing Soil Char Level No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL No No No SL No No SL No No No No SL No No No No SL No No No No No No No No No No SL No No SL No SL No SL No No Ratio Boeing Soil Char Level 1.08E‐02 5.53E‐01 5.79E‐02 3.04E‐03 7.51E‐02 1.76E‐03 3.79E‐03 3.79E‐03 3.79E‐03 5.30E+00 7.86E‐03 6.00E‐04 2.73E‐01 5.94E‐02 2.11E‐04 8.26E‐03 4.22E‐03 1.73E‐01 1.46E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 1.50E‐03 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 2.09E‐03 2.44E‐06 2.08E‐02 2.73E‐05 1.13E‐02 3.17E‐03 8.70E‐04 No SL 6.00E‐04 No SL 1.94E‐03 6.13E‐02 5.77E‐02 4.62E‐05 2.30E‐02 1.37E‐02 1.88E‐03 2.61E‐04 No SL 4.51E‐03 No SL 1.10E+00 4.78E‐04 2.44E‐03 4.78E‐04 5.22E‐02 2.40E‐04 No SL 3.08E‐02 2.61E‐04 1.88E‐03 8.45E‐02 2.86E‐04 No SL 8.19E‐03 1.88E‐03 No SL 6.51E‐04 No SL 8.24E‐04 2.69E‐04 1.46E‐04 No SL 2.60E‐03 4.62E‐03 1.35E‐06 No SL 2.02E‐03 1.82E‐03 9.84E‐05 8.22E‐05 3.75E‐04 1.76E‐03 3.75E‐04 1.62E‐03 6.12E‐03 No SL 2.86E‐05 No SL No SL No SL 5.45E‐03 1.44E‐02 SCL Basis Ecological RBSL MRL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 0.94 0.94 1.9 7.6 37 6 5.3 5.3 5.3 5.3 11 6 6 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 11 11 11 22 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 11 6 6 6 6 6 6 6 6 6 6 6 6 6 55 6 6 6 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg MDL 0.34 0.21 0.37 1.9 12 1 2.1 2.1 2.1 2.1 4.2 1 2 6.4 6.4 6.4 6.4 6.4 6.4 0.71 0.71 0.71 0.71 0.35 0.35 0.71 0.71 0.71 0.71 0.71 0.35 0.71 0.71 0.71 0.71 0.71 0.71 0.71 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 8 0.6 1 1 1 1 2 1 1 2 1 2 2 1 1 1 1 2 1 1 1 4 0.6 2 1 1 1 1 1 1 1 1 1 1 1 22 1 1 1 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2010 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2010S002 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 12:40 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 6850 7199 8315A 1613B 1613B 1613B 9045C 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7471A 8082 8082 8082 Analyte Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal pH 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Page 73 of 108 CAS Number 108883 156605 10061026 79016 75694 75014 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal E‐10139 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7439976 37324235 11100144 12674112 Result  Value 6 6 6 6 6 6 4.3 0.66 2.1 25 29.5 51.9 6.78 81.5 1490 2.98 4.82 19.1 2.78 48.6 1.44 41.6 0.962 9.8 2.65 0.608 0.142 1.1 206 3340 93.9 329 277 42800 21.5 35.3 12 4.05 290 290 570 290 570 290 290 290 290 290 290 380 290 1900 1900 290 290 290 1.7 1.7 36 25 90 12 17 24 2500 2500 0.1 5.5 0.81 7.1 0.4 0.44 6.7 0.17 13400 94 0.537 3.9 17.3 5.44 14.9 315 3100 83.8 30.5 55.4 3.3 0.0865 4.22 0.22 12.6 8.21 0.534 11.9 0.144 0.0261 0.206 0.0096 17 17 17 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.006 mg/kg 0.006 mg/kg 0.006 mg/kg 0.006 mg/kg 0.006 mg/kg 0.006 mg/kg 0.0043 mg/kg 0.43 mg/kg 2.1 mg/kg 0.000025 mg/kg 0.0000295 mg/kg 0.0000519 mg/kg 6.78 ph Units 0.0000815 mg/kg 0.00149 mg/kg 0.00000298 mg/kg 0.00000482 mg/kg 0.0000191 mg/kg 0.00000278 mg/kg 0.0000486 mg/kg 0.00000144 mg/kg 0.0000416 mg/kg 0.000000962 mg/kg 0.0000098 mg/kg 0.00000265 mg/kg 0.000000608 mg/kg 0.000000958 mg/kg 0.0000011 mg/kg 0.000206 mg/kg 0.00000479 mg/kg 0.00000479 mg/kg 0.00000479 mg/kg 0.000277 mg/kg 0.0428 mg/kg 0.00000479 mg/kg 0.00000479 mg/kg 0.000000958 mg/kg 0.000000958 mg/kg 0.29 mg/kg 0.29 mg/kg 0.57 mg/kg 0.29 mg/kg 0.57 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.38 mg/kg 0.29 mg/kg 1.9 mg/kg 1.9 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.036 mg/kg 0.025 mg/kg 0.09 mg/kg 0.012 mg/kg 0.017 mg/kg 0.024 mg/kg 2.5 mg/kg 2.5 mg/kg 2 mg/kg 5.5 mg/kg 0.81 mg/kg 7.1 mg/kg 1 mg/kg 0.44 mg/kg 5 mg/kg 0.48 mg/kg 13400 mg/kg 94 mg/kg 0.537 mg/kg 5.03 mg/kg 17.3 mg/kg 5.44 mg/kg 14.9 mg/kg 315 mg/kg 3100 mg/kg 83.8 mg/kg 30.5 mg/kg 55.4 mg/kg 3.3 mg/kg 0.201 mg/kg 4.22 mg/kg 0.22 mg/kg 12.6 mg/kg 8.21 mg/kg 0.534 mg/kg 11.9 mg/kg 0.144 mg/kg 0.101 mg/kg 0.206 mg/kg 0.0964 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg Detected N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y N Y N N N N Project  Qual  Code U U U U U U U U U J J J J J J U UJ UJ UJ UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U J J J U J U U Validation Note B F F, B F, B F, B F F, B F B F, B F F F, B B F, B M, F, B M, F, B M, F, B F, B F, B M, F, B M, F, B M, F, B M, F, B L Q Q Q Q Q, F Q, Q U B J Q, Q Q J UJ Q, Q Q, Q J J Q, Q, B Q, Q J J U Q, Q U U U U Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 59 No 1.02E‐04 Ecological RBSL 85.3 No 7.03E‐05 Suburban Residential RBSL ‐‐ No SL No SL 0.797 No 7.53E‐03 Suburban Residential RBSL 170 No 3.53E‐05 Ecological RBSL 0.0204 No 2.94E‐01 Suburban Residential RBSL 0.5 No 8.60E‐03 Ecological RBSL 1.29 No 3.33E‐01 Suburban Residential RBSL 43 No 4.88E‐02 Ecological RBSL 0.0000057 Yes 4.39E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 9.22E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.15E‐01 Ecological RBSL 0.3 No 9.67E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 9.67E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 3.45E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 9.67E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.54E‐04 Ecological RBSL 0.55 No 3.09E‐03 Ecological RBSL 1.1 No 3.27E‐02 Ecological RBSL 6.2 No 4.03E‐03 Ecological RBSL 39 No 2.31E‐03 Ecological RBSL 14 No 8.57E‐04 Ecological RBSL 0.79 No 2.15E‐02 Ecological RBSL 0.18 No 1.33E‐01 Ecological RBSL 3.3 No 7.58E‐01 MRL 3.3 No 7.58E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 2.31E‐02 Ecological RBSL 2340 No 3.03E‐03 Ecological RBSL ‐‐ No SL No SL 863.2 No 5.10E‐04 Background ‐‐ No SL No SL 0.5 No 9.60E‐01 MRL 37900 No 3.54E‐01 Background 203.8 No 4.61E‐01 Background 4.8 No 1.12E‐01 Ecological RBSL 22 No 2.29E‐01 Ecological RBSL 60.11 No 2.88E‐01 Background 26.18 No 2.08E‐01 Background 64.4 No 2.31E‐01 Background 723 No 4.36E‐01 Background 7524 No 4.12E‐01 Background 754 No 1.11E‐01 Background 111.8 No 2.73E‐01 Background 153 No 3.62E‐01 Background 10.64 No 3.10E‐01 Background 0.5 No 4.02E‐01 MRL 24.2 No 1.74E‐01 Background 0.435 No 5.06E‐01 Background 42 No 3.00E‐01 Background 33.9 No 2.42E‐01 Background 1.642 No 3.25E‐01 Background 64.2 No 1.85E‐01 Background 1 No 1.44E‐01 MRL 0.99 No 1.02E‐01 Ecological RBSL 0.761 No 2.71E‐01 Suburban Residential RBSL 0.87 No 1.11E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.42E‐01 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 6 6 6 6 6 6 4.3 0.43 2.1 0.01 4.79 4.79 4.79 4.79 4.79 4.79 4.79 4.79 4.79 4.79 4.79 4.79 4.79 0.958 0.958 4.79 4.79 4.79 4.79 9.58 9.58 4.79 4.79 0.958 0.958 290 290 570 290 570 290 290 290 290 290 290 380 290 1900 1900 290 290 290 1.7 1.7 36 25 90 12 17 24 2500 2500 2 5 1 4.4 1 5 5 0.48 10.1 0.503 0.251 5.03 0.754 0.503 2 0.503 50.3 50.3 0.503 2.01 5.03 0.201 0.402 0.101 0.201 0.201 0.101 0.402 0.402 0.101 0.101 0.0964 17 17 17 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg pH Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg MDL 1 1 1 1 2 1 2.2 0.15 1.3 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y 0.01 pH Units Y 0.0449 ng/kg Y 0.311 ng/kg Y 0.0652 ng/kg Y 0.0534 ng/kg Y 0.088 ng/kg Y 0.0515 ng/kg Y 0.0916 ng/kg Y 0.0619 ng/kg Y 0.0974 ng/kg Y 0.0432 ng/kg Y 0.154 ng/kg Y 0.0434 ng/kg Y 0.0453 ng/kg Y 0.0669 ng/kg Y 0.0525 ng/kg Y 0.0532 ng/kg Y 0.311 ng/kg Y 0.0519 ng/kg Y 0.0922 ng/kg Y 0.0523 ng/kg Y 0.261 ng/kg Y 0.0442 ng/kg Y 0.154 ng/kg Y 0.0669 ng/kg Y 0.0525 ng/kg Y 96 ug/kg Y 96 ug/kg Y 190 ug/kg Y 96 ug/kg Y 190 ug/kg Y 96 ug/kg Y 96 ug/kg Y 190 ug/kg Y 240 ug/kg Y 140 ug/kg Y 190 ug/kg Y 240 ug/kg Y 96 ug/kg Y 1400 ug/kg Y 1400 ug/kg Y 120 ug/kg Y 96 ug/kg Y 150 ug/kg Y 0.82 ug/kg Y 0.75 ug/kg Y 12 ug/kg Y 25 ug/kg Y 44 ug/kg Y 4 ug/kg Y 9 ug/kg Y 9 ug/kg Y 760 ug/kg Y 750 ug/kg Y 0.1 mg/kg Y 1 mg/kg Y 0.4 mg/kg Y 1.8 mg/kg Y 0.4 mg/kg Y 0.1 mg/kg Y 1.6 mg/kg Y 0.17 mg/kg Y 7.25 mg/kg Y 0.0332 mg/kg Y 0.0674 mg/kg Y 0.844 mg/kg Y 0.161 mg/kg Y 0.0995 mg/kg Y 0.34 mg/kg Y 0.0834 mg/kg Y 8.38 mg/kg Y 16.8 mg/kg Y 0.131 mg/kg Y 0.201 mg/kg Y 0.844 mg/kg Y 0.0865 mg/kg Y 0.0844 mg/kg Y 0.0462 mg/kg Y 0.0965 mg/kg Y 0.0161 mg/kg Y 0.0503 mg/kg Y 0.0764 mg/kg Y 0.101 mg/kg Y 0.0261 mg/kg Y 0.0302 mg/kg Y 0.0096 mg/kg Y 3.3 ug/kg Y 3.3 ug/kg Y 3.6 ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S001 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S002 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:30 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 8:45 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Metals VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 7199 8315A 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate Hexavalent Chromium Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran Page 74 of 108 CAS Number 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 18540299 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 Result  Value 17 17 17 17 5.9 17 1.8 2.9 3.4 0.83 0.83 1 17 0.83 1.7 0.55 0.83 1.7 0.5 0.47 1.8 0.83 3.3 0.83 0.77 6.7 33 5.1 5.1 5.1 5.1 10 18 18 18 18 18 18 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 4.1 0.37 2 4.66 5.87 10.6 5.4 5.4 4.9 5.4 19 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.1 1.8 1.8 2.3 1.8 0.86 4.5 1.8 12 1.8 1.8 1.8 7.9 8.4 16.5 327 0.67 1.19 4.36 0.358 11 0.337 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.0059 mg/kg 0.017 mg/kg 0.0018 mg/kg 0.0029 mg/kg 0.0034 mg/kg 0.00083 mg/kg 0.00083 mg/kg 0.001 mg/kg 0.017 mg/kg 0.00083 mg/kg 0.0017 mg/kg 0.00055 mg/kg 0.00083 mg/kg 0.0017 mg/kg 0.0005 mg/kg 0.00047 mg/kg 0.0018 mg/kg 0.00083 mg/kg 0.0033 mg/kg 0.00083 mg/kg 0.00077 mg/kg 0.0067 mg/kg 0.033 mg/kg 5.1 mg/kg 5.1 mg/kg 5.1 mg/kg 5.1 mg/kg 10 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0041 mg/kg 0.41 mg/kg 2 mg/kg 0.00000466 mg/kg 0.00000587 mg/kg 0.0000106 mg/kg 5.4 mg/kg 5.4 mg/kg 4.9 mg/kg 5.4 mg/kg 19 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0011 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0023 mg/kg 0.0018 mg/kg 0.00086 mg/kg 0.0045 mg/kg 0.0018 mg/kg 0.012 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0079 mg/kg 0.0084 mg/kg 0.0000165 mg/kg 0.000327 mg/kg 0.00000067 mg/kg 0.00000119 mg/kg 0.00000436 mg/kg 0.00000534 mg/kg 0.000011 mg/kg 0.00000534 mg/kg Detected N N N N Y N Y Y Y N N N N N N Y N N Y Y N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N N Y N Y N N N N N N N N N N N Y N N Y N Y Y N Y N N N Y Y Y Y Y Y Y N Y N Project  Qual  Code U U U U J U J J J U U U U U U J U U J J U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U J U U U U U U U U U U U J U U Validation Note S S S S S S S S S S S S S S S S S S S S S F B Q, Q Q, Q F U J U U U U J J J J UJ U L F, B Q, Q, Q, F, B F, B F, B F, B M, F, B B F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.18 No 9.44E‐02 Ecological RBSL 0.082 No 2.07E‐01 Ecological RBSL 0.043 No 3.95E‐01 Ecological RBSL 0.017 No 1.00E+00 MRL 0.039 No 1.51E‐01 Ecological RBSL 0.025 No 6.80E‐01 Ecological RBSL 0.0051 No 3.53E‐01 Ecological RBSL 0.004164 No 6.96E‐01 Background 0.006101 No 5.57E‐01 Background 0.0348 No 2.39E‐02 Suburban Residential RBSL 0.073 No 1.14E‐02 Ecological RBSL 0.394 No 2.54E‐03 Suburban Residential RBSL 1.1 No 1.55E‐02 Ecological RBSL 0.067 No 1.24E‐02 Ecological RBSL 0.013 No 1.31E‐01 Ecological RBSL 0.23 No 2.39E‐03 Ecological RBSL 0.22 No 3.77E‐03 Ecological RBSL 0.22 No 7.73E‐03 Ecological RBSL 0.0079 No 6.33E‐02 Ecological RBSL 0.0092 No 5.11E‐02 Ecological RBSL 0.0086 No 2.09E‐01 Ecological RBSL 0.075 No 1.11E‐02 Ecological RBSL 0.087 No 3.79E‐02 Ecological RBSL 0.0017 No 4.88E‐01 MRL 0.0328 No 2.35E‐02 Suburban Residential RBSL 2.5 No 2.68E‐03 Ecological RBSL 0.493 No 6.69E‐02 Suburban Residential RBSL 1400 No 3.64E‐03 1400 No 3.64E‐03 1400 No 3.64E‐03 1 Yes 5.10E+00 1400 No 7.14E‐03 0.32 No 5.63E‐02 Ecological RBSL 90 No 2.00E‐04 Ecological RBSL 2.3 No 7.83E‐03 Ecological RBSL 4.5 No 4.00E‐03 Ecological RBSL 0.11 No 1.64E‐01 Ecological RBSL 13 No 1.38E‐03 Ecological RBSL 0.0325 No 5.23E‐02 Suburban Residential RBSL 7.29 No 2.33E‐04 Suburban Residential RBSL 53 No 3.21E‐05 Ecological RBSL 1.1 No 1.55E‐03 Ecological RBSL 0.33 No 5.15E‐03 Ecological RBSL 2.2 No 7.73E‐04 Ecological RBSL 0.387 No 4.39E‐03 Suburban Residential RBSL 0.0387 No 4.39E‐02 Suburban Residential RBSL 0.387 No 4.39E‐03 Suburban Residential RBSL 7.4 No 2.30E‐04 Ecological RBSL 0.387 No 4.39E‐03 Suburban Residential RBSL 1.2 No 1.42E‐03 Ecological RBSL 0.113 No 1.50E‐02 Suburban Residential RBSL 54 No 3.15E‐05 Ecological RBSL 0.89 No 1.91E‐03 Ecological RBSL 0.387 No 4.39E‐03 Suburban Residential RBSL 14.6 No 1.16E‐04 Suburban Residential RBSL 1.3 No 1.31E‐03 Ecological RBSL 1.2 No 1.42E‐03 Ecological RBSL 0.5 No 8.20E‐03 Ecological RBSL 1.29 No 3.18E‐01 Suburban Residential RBSL 43 No 4.65E‐02 Ecological RBSL 0.0000057 No 8.18E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.88E+01 Background 1400 No 3.86E‐03 1400 No 3.86E‐03 1400 No 3.50E‐03 1 Yes 5.40E+00 1400 No 1.36E‐02 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 1.46E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 5.45E‐03 Ecological RBSL 2.2 No 5.00E‐04 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 0.0387 No 4.65E‐02 Suburban Residential RBSL 0.387 No 5.94E‐03 Suburban Residential RBSL 7.4 No 2.43E‐04 Ecological RBSL 0.387 No 2.22E‐03 Suburban Residential RBSL 1.2 No 3.75E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 2.22E‐04 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 14.6 No 1.23E‐04 Suburban Residential RBSL 1.3 No 6.08E‐03 Ecological RBSL 1.2 No 7.00E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 17 17 17 17 17 17 1.7 1.7 1.7 0.83 0.83 1 17 0.83 1.7 1.7 0.83 1.7 1.7 1.7 1.8 0.83 3.3 0.83 1.7 6.7 33 5.1 5.1 5.1 5.1 10 18 18 18 18 18 18 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 4.1 0.41 2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 4.6 8 3.3 3.3 3.3 4.9 0.33 0.33 0.33 0.33 0.17 0.3 4 0.18 0.33 0.33 0.22 0.33 0.33 0.33 1.2 0.17 3.3 0.19 0.33 1.7 11 2 2 2 2 4.1 6.1 6.1 6.1 6.1 6.1 6.1 0.68 0.68 0.68 0.68 0.34 0.34 0.68 0.68 0.68 0.68 0.68 0.34 0.68 0.68 0.68 0.68 0.68 0.68 0.68 2.1 0.14 1.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg 5.4 5.4 5.4 5.4 11 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 5.34 5.34 5.34 5.34 5.34 5.34 5.34 5.34 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 2.2 2.2 2.2 2.2 4.3 6.5 6.5 6.5 6.5 6.5 6.5 0.72 0.72 0.72 0.72 0.36 0.36 0.72 0.72 0.72 0.72 0.72 0.36 0.72 0.72 0.72 0.72 0.72 0.72 0.72 0.0282 0.272 0.0396 0.038 0.0866 0.036 0.0916 0.0412 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6850 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7199 7471A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A Analyte 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Perchlorate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Hexavalent Chromium Mercury Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Page 75 of 108 CAS Number 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 14797730 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 18540299 7439976 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 Result  Value 8.3 0.202 1.93 0.534 0.212 0.042 0.147 41.8 710 18 69.5 62.1 8900 2.89 6.42 0.906 0.68 320 320 650 320 650 320 320 320 320 320 320 430 320 2200 2200 320 320 320 1.8 1.8 39 18 97 13 18 26 2700 2700 0.11 24.7 0.43 21 0.43 0.27 14.4 4.3 0.19 19500 91.1 0.869 6.42 23.3 7.01 31.1 296 2300 103 47.1 51.7 4.17 0.091 12.5 0.0979 9.11 10.9 0.256 15.6 0.106 0.0426 0.254 0.56 0.0107 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.89 0.89 1.1 18 0.89 1.8 1.8 0.89 1.8 1.8 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.0000083 mg/kg 0.00000534 mg/kg 0.00000193 mg/kg 0.000000534 mg/kg 0.00000534 mg/kg 0.00000107 mg/kg 0.00000107 mg/kg 0.00000534 mg/kg 0.00071 mg/kg 0.00000534 mg/kg 0.0000695 mg/kg 0.0000621 mg/kg 0.0089 mg/kg 0.00000534 mg/kg 0.00000534 mg/kg 0.00000107 mg/kg 0.00000107 mg/kg 0.32 mg/kg 0.32 mg/kg 0.65 mg/kg 0.32 mg/kg 0.65 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.43 mg/kg 0.32 mg/kg 2.2 mg/kg 2.2 mg/kg 0.32 mg/kg 0.32 mg/kg 0.32 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.039 mg/kg 0.018 mg/kg 0.097 mg/kg 0.013 mg/kg 0.018 mg/kg 0.026 mg/kg 2.7 mg/kg 2.7 mg/kg 2.2 mg/kg 24.7 mg/kg 1.1 mg/kg 21 mg/kg 1.1 mg/kg 0.27 mg/kg 14.4 mg/kg 0.0043 mg/kg 0.53 mg/kg 19500 mg/kg 91.1 mg/kg 0.869 mg/kg 6.42 mg/kg 23.3 mg/kg 7.01 mg/kg 31.1 mg/kg 296 mg/kg 2300 mg/kg 103 mg/kg 47.1 mg/kg 51.7 mg/kg 4.17 mg/kg 0.212 mg/kg 12.5 mg/kg 0.0979 mg/kg 9.11 mg/kg 10.9 mg/kg 0.256 mg/kg 15.6 mg/kg 0.423 mg/kg 0.0426 mg/kg 0.254 mg/kg 0.43 mg/kg 0.107 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00089 mg/kg 0.00089 mg/kg 0.0011 mg/kg 0.018 mg/kg 0.00089 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00089 mg/kg 0.0018 mg/kg 0.0018 mg/kg Detected Y N Y Y N N N N Y N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code U J J UJ U UJ UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U J UJ J U J J U U Validation Note B F, B F, B F, B M, F, B M, B M, F, B F, B M, F, B F, B Q, Q, F, B Q, Q, F, B M, F, B M, F, B M, F, B M, F, B Q, Q, L Q Q Q Q Q, F Q, Q B J J UJ J J J Q, Q Q Q, Q Q, Q Q, Q, B Q, Q J U J Q, Q U U U U U U U U U U U U U U U U U U U U U U U U B Q, Q Q Q Q, Q Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 1.29 0.87 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.48E‐01 1.07E+00 No SL No SL No SL No SL 1.07E+00 No SL No SL No SL No SL 3.91E‐03 No SL No SL No SL 1.07E+00 No SL No SL 3.75E‐04 3.27E‐03 3.55E‐02 2.90E‐03 2.49E‐03 9.29E‐04 2.28E‐02 1.44E‐01 8.18E‐01 8.18E‐01 No SL No SL 3.14E‐02 8.97E‐03 No SL 3.13E‐04 No SL 8.60E‐03 1.06E+00 5.15E‐01 4.47E‐01 1.81E‐01 2.92E‐01 3.88E‐01 2.68E‐01 4.83E‐01 4.09E‐01 3.06E‐01 1.37E‐01 4.21E‐01 3.38E‐01 3.92E‐01 4.24E‐01 5.17E‐01 2.25E‐01 2.17E‐01 3.22E‐01 1.56E‐01 2.43E‐01 4.23E‐01 4.30E‐02 3.34E‐01 3.33E‐01 1.23E‐01 No SL No SL 1.50E‐01 1.00E‐01 2.20E‐01 4.19E‐01 1.06E+00 4.62E‐01 7.20E‐01 3.53E‐01 4.32E‐01 2.95E‐01 2.56E‐02 1.22E‐02 2.79E‐03 1.64E‐02 1.33E‐02 1.38E‐01 7.83E‐03 4.05E‐03 8.18E‐03 2.28E‐01 SCL Basis Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background Ecological RBSL MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 5.34 5.34 5.34 5.34 5.34 1.07 1.07 5.34 5.34 5.34 5.34 10.7 10.7 5.34 5.34 1.07 1.07 320 320 650 320 650 320 320 320 320 320 320 430 320 2200 2200 320 320 320 1.8 1.8 39 18 97 13 18 26 2700 2700 2.2 26.9 1.1 4.9 1.1 5.4 5.4 4.3 0.53 10.6 0.529 0.264 5.29 0.793 0.529 2.1 0.529 52.9 52.9 0.529 2.12 5.29 0.212 0.423 0.106 0.212 0.212 0.106 0.423 0.423 0.106 0.106 0.43 0.107 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.89 0.89 1.1 18 0.89 1.8 1.8 0.89 1.8 1.8 RL Units MDL ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0899 0.031 0.0762 0.0366 0.0293 0.042 0.0456 0.0329 0.272 0.0379 0.0893 0.0411 0.0924 0.0301 0.0762 0.042 0.0456 110 110 220 110 220 110 110 220 270 160 220 270 110 1600 1600 130 110 170 0.88 0.81 13 6.7 47 4.3 9.7 9.7 820 810 0.11 5.4 0.43 1.9 0.43 0.11 1.7 2.3 0.19 7.63 0.0349 0.0709 0.888 0.169 0.105 0.36 0.0878 8.82 17.7 0.137 0.212 0.888 0.091 0.0888 0.0486 0.102 0.0169 0.0529 0.0804 0.106 0.0275 0.0317 0.15 0.0107 3.6 3.6 3.9 5 8.6 3.6 3.6 3.6 5.3 0.35 0.35 0.35 0.35 0.18 0.32 4.3 0.19 0.35 0.35 0.24 0.35 0.35 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N Y N Y Y Y N N N N N N Y N Y N N N N N N N N Y N N N N Y Y N N Y N N N N N Y Y N Y N Y Y N N N Y Y N Y Y Y Y Y Y Y Y Y N Y N Y Y Y Y Y N Y N N N N N N N N N N N N N N N N N N N N N N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date Matrix  Type 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:15 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Lab Repeat Analysis Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8015B 8015B 8015B 8015B 6010B 6850 9012B 9056 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 Analyte Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans sym‐Trinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 4‐Amino‐2,6‐Dinitrotoluene HMX 1,3‐Dinitrobenzene 3‐Nitrotoluene Nitrobenzene 2‐Nitrotoluene PETN 4‐Nitrotoluene RDX Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Phosphorus Perchlorate Cyanides Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Antimony Barium Boron Calcium Chromium Cobalt Iron Manganese Potassium Silver Sodium Strontium Tin Titanium Vanadium Zinc Aluminum Arsenic Beryllium Cadmium Copper Lead Page 76 of 108 CAS Number 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 51207319 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 99354 118967 6629294 121142 59229753 606202 35572782 19406510 2691410 99650 99081 98953 88722 78115 99990 121824 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 7723140 14797730 57125 24959679 16887006 16984488 NO3 NO2 14265442 14808798 7440360 7440393 7440428 7440702 7440473 7440484 7439896 7439965 7440097 7440224 7440235 7440246 7440315 7440326 7440622 7440666 7429905 7440382 7440417 7440439 7440508 7439921 Result  Value 1.8 1.9 0.89 0.89 0.89 1.8 7.2 35 2.2 0.859 0.587 2.99 0.307 5.73 126 0.425 0.534 1.34 0.291 3.58 0.3 3.02 0.207 0.787 0.307 0.176 0.114 0.089 19.5 3360 302 17 27.5 8.27 2.72 1.49 0.114 0.089 149 149 1990 149 1990 149 149 149 149 149 149 149 149 498 149 149 149 5.47 5.47 5.47 5.47 109 5.47 5.47 5.47 1090 1090 1.82 1.82 1.82 1.82 106 2.17 0.0915 0.735 2.67 2.01 0.551 0.362 0.735 3.64 1.09 88.1 10.1 2440 18.7 5.01 18300 184 1770 0.239 96 23.4 0.384 837 35.4 42.3 20300 7.27 0.692 0.167 7.72 6.35 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.0018 mg/kg 0.0019 mg/kg 0.00089 mg/kg 0.00089 mg/kg 0.00089 mg/kg 0.0018 mg/kg 0.0072 mg/kg 0.035 mg/kg 2.2 mg/kg 0.000000859 mg/kg 0.000000587 mg/kg 0.00000299 mg/kg 0.000000908 mg/kg 0.00000573 mg/kg 0.000126 mg/kg 0.00000454 mg/kg 0.00000454 mg/kg 0.00000454 mg/kg 0.00000454 mg/kg 0.00000358 mg/kg 0.00000454 mg/kg 0.00000302 mg/kg 0.00000454 mg/kg 0.00000454 mg/kg 0.00000454 mg/kg 0.00000454 mg/kg 0.000000908 mg/kg 0.000000908 mg/kg 0.0000195 mg/kg 0.00336 mg/kg 0.000302 mg/kg 0.00000454 mg/kg 0.0000275 mg/kg 0.00000827 mg/kg 0.00000272 mg/kg 0.00000454 mg/kg 0.000000114 mg/kg 0.000000089 mg/kg 0.149 mg/kg 0.149 mg/kg 1.99 mg/kg 0.149 mg/kg 1.99 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.498 mg/kg 0.149 mg/kg 0.149 mg/kg 0.149 mg/kg 0.00547 mg/kg 0.00547 mg/kg 0.00547 mg/kg 0.00547 mg/kg 0.109 mg/kg 0.00547 mg/kg 0.00547 mg/kg 0.00547 mg/kg 1.09 mg/kg 1.09 mg/kg 1.82 mg/kg 1.82 mg/kg 1.82 mg/kg 1.82 mg/kg 106 mg/kg 0.00217 mg/kg 0.274 mg/kg 2.19 mg/kg 2.67 mg/kg 2.01 mg/kg 0.551 mg/kg 1.1 mg/kg 2.19 mg/kg 4.39 mg/kg 1.02 mg/kg 88.1 mg/kg 10.1 mg/kg 2440 mg/kg 18.7 mg/kg 5.01 mg/kg 18300 mg/kg 184 mg/kg 1770 mg/kg 0.239 mg/kg 96 mg/kg 23.4 mg/kg 0.384 mg/kg 837 mg/kg 35.4 mg/kg 42.3 mg/kg 20300 mg/kg 7.27 mg/kg 0.692 mg/kg 0.167 mg/kg 7.72 mg/kg 6.35 mg/kg Detected N N N N N N N N N Y Y Y N Y Y N N N N Y N Y N N N N N N Y Y Y N Y Y Y N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N Y Y Y N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Project  Qual  Code Validation Note U U U U U U U U U U U U U U J U J UJ U U U U U UJ J UJ J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U D, B F, B F, B F, B F, B F, B F, B B F, B B M, F, B F, B F, B F, B B B F, B F, B F, B M, F, B F, B F, B F, B M, F, B F, B F, B L L L L U U U J U U U U F B J J J B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.19E‐02 Ecological RBSL 0.087 No 1.02E‐02 Ecological RBSL 0.0017 No 5.24E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.88E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 43 No 5.12E‐02 Ecological RBSL 0.0000057 No 1.51E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 5.31E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 4.97E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 4.97E‐01 MRL ‐‐ No SL No SL 110 No 1.35E‐03 Ecological RBSL 0.92 No 1.62E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 4.97E‐01 Ecological RBSL ‐‐ No SL No SL 4.8 No 1.14E‐03 Ecological RBSL 0.55 No 9.95E‐03 Ecological RBSL 1.1 No 4.97E‐03 Ecological RBSL 6.2 No 8.82E‐04 Ecological RBSL 39 No 2.79E‐03 Ecological RBSL 14 No 3.91E‐04 Ecological RBSL 0.79 No 6.92E‐03 Ecological RBSL 0.18 No 3.04E‐02 Ecological RBSL 3.3 No 3.30E‐01 MRL 3.3 No 3.30E‐01 MRL 1400 No 1.30E‐03 1400 No 1.30E‐03 1400 No 1.30E‐03 1 Yes 1.82E+00 ‐‐ No SL No SL 0.5 No 4.34E‐03 Ecological RBSL 0.5 No 5.48E‐01 MRL ‐‐ No SL No SL No SL ‐‐ No SL 35 No 5.74E‐02 Ecological RBSL 2340 No 2.35E‐04 Ecological RBSL ‐‐ No SL No SL 863.2 No 2.54E‐03 Background ‐‐ No SL No SL 0.5 Yes 2.04E+00 MRL 203.8 No 4.32E‐01 Background 22 No 4.59E‐01 Ecological RBSL ‐‐ No SL No SL 60.11 No 3.11E‐01 Background 26.18 No 1.91E‐01 Background ‐‐ No SL No SL 723 No 2.54E‐01 Background 7524 No 2.35E‐01 Background 0.99 No 2.41E‐01 Ecological RBSL 754 No 1.27E‐01 Background 1210 No 1.93E‐02 Ecological RBSL 31 No 1.24E‐02 Ecological RBSL 1865 No 4.49E‐01 Background 111.8 No 3.17E‐01 Background 153 No 2.76E‐01 Background 37900 No 5.36E‐01 Background 24.2 No 3.00E‐01 Background 4.8 No 1.44E‐01 Ecological RBSL 0.435 No 3.84E‐01 Background 42 No 1.84E‐01 Background 33.9 No 1.87E‐01 Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.8 1.9 0.89 0.89 0.89 1.8 7.2 35 2.2 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.908 4.54 4.54 4.54 4.54 4.54 4.54 4.54 4.54 4.54 4.54 4.54 4.54 4.54 0.908 0.908 9.08 9.08 4.54 4.54 4.54 4.54 4.54 4.54 0.908 0.908 149 149 1990 149 1990 149 149 149 149 149 149 149 149 498 149 149 149 5.47 5.47 5.47 5.47 109 5.47 5.47 5.47 1090 1090 1.82 1.82 1.82 1.82 15.3 2.17 0.274 2.19 2.19 1.1 1.1 1.1 2.19 4.39 1.02 0.511 5.11 25.6 0.511 0.511 25.6 1.02 25.6 0.511 25.6 0.511 1.02 0.511 0.511 1.02 101 1.01 0.101 0.203 0.203 0.405 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL 0.35 0.35 0.18 0.32 0.2 0.35 1.8 12 1.3 49.8 49.8 498 49.8 657 49.8 49.8 49.8 49.8 49.8 49.8 49.8 49.8 82.1 49.8 49.8 49.8 1.81 1.81 1.81 1.81 38.3 2.19 2.47 1.81 251 219 0.601 0.601 0.601 0.601 5.11 0.543 0.0915 0.735 0.735 0.362 0.362 0.362 0.735 1.46 0.338 0.102 1.02 8.18 0.153 0.153 8.18 0.205 6.55 0.102 7.16 0.102 0.307 0.102 0.102 0.409 30.4 0.203 0.0203 0.0203 0.0669 0.101 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N Y N Y N N N N N N N N N Y N Y N N N N Y Y N N N N Y N Y Y Y Y Y Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N Y Y Y Y Y Y Y N Y Y Y Y N N Y N Y N N Y N Y Y N N Y N N Y N Y Y Y N N Y N N Y N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S003SP ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 ELBS2012S004 Object Type ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 ELBS2012S003 Sample ID Sample Type Collection  Date Matrix  Type Sample Top  Depth (feet bgs) Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 9:20 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 6/20/13 10:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 Remediation  Status Result Type Analytical Class In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 6020 6020 6020 6020 6020 6020 6020 7196A 7471A 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte CAS Number Lithium Magnesium Molybdenum Nickel Selenium Thallium Zirconium Hexavalent Chromium Mercury bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1268 Aroclor 5432 Aroclor 5442 Aroclor 5460 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1262 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan I Endosulfan II Endosulfan sulfate Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Methoxychlor Mirex Toxaphene Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 7439932 7439954 7439987 7440020 7782492 7440280 7440677 18540299 7439976 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 11100144 63496311 12642238 11126424 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 72548 72559 50293 309002 319846 319857 57749 319868 60571 959988 33213659 1031078 72208 7421934 53494705 58899 76448 1024573 72435 2385855 8001352 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 Result  Value 28.9 4170 0.232 13.6 0.334 0.236 2.51 0.172 0.00948 188 188 188 188 188 188 188 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 2.64 3.77 3.77 3.77 3.77 1.51 3.62 18.1 18.1 7.06 3.62 3.62 3.62 3.62 3.62 24.2 11.2 3.62 1.45 1.45 1.45 0.723 0.723 0.723 9.04 0.723 1.45 0.723 1.45 1.45 1.45 1.45 1.45 0.723 0.723 0.723 7.23 0.723 18.1 2.5 0.0374 0.0374 0.191 0.469 8.68 0.0765 0.0803 0.154 0.0645 0.388 0.0979 0.299 0.0247 0.134 0.0418 0.0248 0.0457 0.058 1.35 20 6.01 2.98 1.62 200 Result  Value  Units Result  in SL Units SL Units Detected mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 28.9 mg/kg 4170 mg/kg 0.232 mg/kg 13.6 mg/kg 1.01 mg/kg 0.236 mg/kg 2.51 mg/kg 0.43 mg/kg 0.00948 mg/kg 0.188 mg/kg 0.188 mg/kg 0.188 mg/kg 0.188 mg/kg 0.188 mg/kg 0.188 mg/kg 0.188 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00264 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00377 mg/kg 0.00151 mg/kg 0.00362 mg/kg 0.0181 mg/kg 0.0181 mg/kg 0.00706 mg/kg 0.00362 mg/kg 0.00362 mg/kg 0.00362 mg/kg 0.00362 mg/kg 0.00362 mg/kg 0.0242 mg/kg 0.0112 mg/kg 0.00362 mg/kg 0.00145 mg/kg 0.00145 mg/kg 0.00145 mg/kg 0.000723 mg/kg 0.000723 mg/kg 0.000723 mg/kg 0.00904 mg/kg 0.000723 mg/kg 0.00145 mg/kg 0.000723 mg/kg 0.00145 mg/kg 0.00145 mg/kg 0.00145 mg/kg 0.00145 mg/kg 0.00145 mg/kg 0.000723 mg/kg 0.000723 mg/kg 0.000723 mg/kg 0.00723 mg/kg 0.000723 mg/kg 0.0181 mg/kg 2.5 mg/kg 3.74E‐08 mg/kg 3.74E‐08 mg/kg 0.000000191 mg/kg 0.000000469 mg/kg 0.00000868 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.000000388 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.0000012 mg/kg 0.0000012 mg/kg 0.00000135 mg/kg 0.00002 mg/kg 0.00000601 mg/kg 0.00000298 mg/kg 0.00000162 mg/kg 0.0002 mg/kg Y Y Y Y N Y Y N Y N N N N N N N N N N N N N N N N N N N Y N N N N Y N N N Y N N N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y N N N N Y N N N N N N N N Y Y Y Y Y Y Project  Qual  Code Validation Note U J U J U U U U U U U U U U U U U U U U U U U J U U U U J U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ J UJ U U UJ J UJ UJ U U UJ U U U J J J J F L L H , F, B , F, B , F, B, M , F, B B, F , F, B, M , B , F, B, M , B, M F, B , F, B , F, B, M F, B B , F, B , F, B , F, B, Original Result = 1.1 , F, B , F, B , F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 64.4 No 4.49E‐01 Background ‐‐ No SL No SL 1.642 No 1.41E‐01 Background 64.2 No 2.12E‐01 Background 1 Yes 1.01E+00 MRL 0.761 No 3.10E‐01 Suburban Residential RBSL 10.64 No 2.36E‐01 Background 1.29 No 3.33E‐01 Suburban Residential RBSL 0.87 No 1.09E‐02 Ecological RBSL 0.32 No 5.88E‐01 Ecological RBSL 90 No 2.09E‐03 Ecological RBSL 2.3 No 8.17E‐02 Ecological RBSL 4.5 No 4.18E‐02 Ecological RBSL 0.11 Yes 1.71E+00 Ecological RBSL 13 No 1.45E‐02 Ecological RBSL 0.0325 Yes 5.78E+00 Suburban Residential RBSL 7.29 No 5.17E‐04 Suburban Residential RBSL 53 No 7.11E‐05 Ecological RBSL 1.1 No 3.43E‐03 Ecological RBSL 0.33 No 1.14E‐02 Ecological RBSL 2.2 No 1.71E‐03 Ecological RBSL 0.387 No 9.74E‐03 Suburban Residential RBSL 0.0387 No 9.74E‐02 Suburban Residential RBSL 0.387 No 9.74E‐03 Suburban Residential RBSL 7.4 No 5.09E‐04 Ecological RBSL 0.387 No 9.74E‐03 Suburban Residential RBSL 1.2 No 3.14E‐03 Ecological RBSL 0.113 No 3.34E‐02 Suburban Residential RBSL 54 No 4.89E‐05 Ecological RBSL 0.89 No 4.24E‐03 Ecological RBSL 0.387 No 9.74E‐03 Suburban Residential RBSL 14.6 No 2.58E‐04 Suburban Residential RBSL 1.3 No 2.90E‐03 Ecological RBSL 1.2 No 1.26E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.05 No 1.41E‐01 MRL 0.12 No 3.02E‐02 Ecological RBSL 0.18 No 2.01E‐02 Ecological RBSL 0.082 No 4.41E‐02 Ecological RBSL 0.043 No 8.42E‐02 Ecological RBSL 0.017 No 2.13E‐01 MRL 0.039 No 6.21E‐01 Ecological RBSL 0.025 No 4.48E‐01 Ecological RBSL ‐‐ No SL No SL 0.0051 No 2.84E‐01 Ecological RBSL 0.004164 No 3.48E‐01 Background 0.006101 No 2.38E‐01 Background 0.0348 No 2.08E‐02 Suburban Residential RBSL 0.073 No 9.90E‐03 Ecological RBSL 0.394 No 1.84E‐03 Suburban Residential RBSL 1.1 No 8.22E‐03 Ecological RBSL 0.067 No 1.08E‐02 Ecological RBSL 0.013 No 1.12E‐01 Ecological RBSL 0.22 No 3.29E‐03 Ecological RBSL 0.22 No 6.59E‐03 Ecological RBSL 0.23 No 6.30E‐03 Ecological RBSL 0.0079 No 1.84E‐01 Ecological RBSL 0.0092 No 1.58E‐01 Ecological RBSL 0.0086 No 1.69E‐01 Ecological RBSL 0.075 No 9.64E‐03 Ecological RBSL 0.087 No 8.31E‐03 Ecological RBSL 0.0017 No 4.25E‐01 MRL 2.5 No 2.89E‐03 Ecological RBSL 0.0328 No 2.20E‐02 Suburban Residential RBSL 0.493 No 3.67E‐02 Suburban Residential RBSL 43 No 5.81E‐02 Ecological RBSL 0.0000057 No 6.56E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 3.39E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 2.03 6.08 0.203 0.405 1.01 0.405 0.405 0.43 0.0129 188 188 188 188 188 188 188 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.77 3.62 18.1 18.1 18.1 3.62 3.62 3.62 3.62 3.62 3.62 3.62 3.62 1.45 1.45 1.45 0.723 0.723 0.723 9.04 0.723 1.45 0.723 1.45 1.45 1.45 1.45 1.45 0.723 0.723 0.723 7.23 0.723 18.1 2.5 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 1.2 1.2 6.01 6.01 6.01 6.01 12 12 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg MDL 0.405 2.03 0.0608 0.101 0.334 0.0608 0.101 0.172 0.00432 56.3 56.3 56.3 56.3 56.3 56.3 56.3 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.943 0.566 0.943 0.943 1.21 3.62 3.62 3.62 1.21 1.21 1.21 1.21 1.21 1.21 1.21 1.21 0.361 0.361 0.361 0.181 0.181 0.181 1.81 0.181 0.361 0.181 0.361 0.361 0.361 0.361 0.361 0.181 0.181 0.181 1.81 0.181 6.02 0.016 0.0523 0.0222 0.0281 0.0371 0.0264 0.0395 0.0289 0.0384 0.0247 0.0412 0.027 0.0248 0.0457 0.058 0.0185 0.0523 0.0275 0.0382 0.0375 0.0652 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y EEL EEL CC 1 Soil Boring ELBS2012 ELBS2012S004 Primary Sample 6/20/13 10:00 Soil 9 10 In Place Primary Result HZ Dioxin_Furans 1613B Pentachlorodibenzofurans 30402154 6.01 ng/kg 0.00000601 mg/kg Y J , F, B, Original Result = 0.572 ‐‐ No SL No SL mg/kg 6.01 ng/kg 0.0248 ng/kg Y EEL EEL CC 1 Soil Boring ELBS2012 ELBS2012S004 Primary Sample 6/20/13 10:00 Soil 9 10 In Place Primary Result HZ Dioxin_Furans 1613B Pentachlorodibenzo‐p‐dioxins 36088229 6.01 ng/kg 0.00000601 mg/kg Y J , F, B, Original Result = 0.914 ‐‐ No SL No SL mg/kg 6.01 ng/kg 0.0412 ng/kg Y Y EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Soil Boring Soil Boring Soil Boring Soil Boring ELBS2012 ELBS2012 ELBS2015 ELBS2015 ELBS2012S004 ELBS2012S004 ELBS2015S001 ELBS2015S001 Primary Sample Primary Sample Primary Sample Primary Sample 6/20/13 10:00 6/20/13 10:00 6/17/13 14:15 6/17/13 14:15 10 10 1.5 1.5 Primary Result HZ Primary Result HZ Primary Result Primary Result Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) 55722275 41903575 EFHD (C12‐C14) EFHD (C15‐C20) 0.0000012 mg/kg 0.0000012 mg/kg 10 mg/kg 10 mg/kg Y Y N N J J U U , F, B, Original Result = 0.402 , F, B, Original Result = 0.67 ‐‐ ‐‐ 1400 1400 No SL No SL No No No SL No SL 7.14E‐03 7.14E‐03 mg/kg mg/kg mg/kg mg/kg 0.0457 0.058 4.2 4.2 Y Y Y Y Y Y Y Y Soil Soil Soil Soil 9 9 0.5 0.5 In Place In Place In Place In Place 1613B 1613B 8015B 8015B Page 77 of 108 1.2 1.2 10 10 ng/kg ng/kg mg/kg mg/kg 1.2 1.2 10 10 ng/kg ng/kg mg/kg mg/kg ng/kg ng/kg mg/kg mg/kg Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2015 ELBS2016 ELBS2017 ELBS2018 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S001 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2015S002 ELBS2016S001 ELBS2017S001 ELBS2018S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:15 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/17/13 14:20 6/14/13 8:20 6/19/13 11:45 6/13/13 13:45 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 5 0 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 0.5 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Arsenic Silver Arsenic DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran Page 78 of 108 CAS Number EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7440382 7440224 7440382 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 Result  Value 33 10 63 19 19 19 19 19 19 1.7 1.7 1.7 1.7 1.7 0.58 3.4 3.8 5.8 3.1 2.7 5.7 0.93 6.5 1.7 1.9 1.7 2.2 5.7 6.3 6.3 6.3 6.3 13 23 23 23 23 23 23 2.1 0.89 2.1 2.1 2.1 2.1 1.2 1.3 2 2.1 1.1 2.3 2.1 2.7 2.1 2.1 0.86 1.6 2.5 24200 99.6 0.798 7.27 26.5 4.72 31.1 187 1890 288 43.7 45.1 5.47 0.151 7.98 0.106 9.56 6.96 0.232 15.6 0.122 0.0891 0.216 7.31 0.0449 22.2 0.108 0.0664 0.157 0.481 1.72 0.095 0.135 0.0577 0.115 0.311 0.497 0.467 0.319 0.12 0.0678 0.0871 0.0554 Result  Value  Units mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 33 mg/kg 10 mg/kg 63 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.00058 mg/kg 0.0034 mg/kg 0.0038 mg/kg 0.0058 mg/kg 0.0031 mg/kg 0.0027 mg/kg 0.0057 mg/kg 0.00093 mg/kg 0.0065 mg/kg 0.0017 mg/kg 0.0019 mg/kg 0.0017 mg/kg 0.0022 mg/kg 0.0017 mg/kg 6.3 mg/kg 6.3 mg/kg 6.3 mg/kg 6.3 mg/kg 13 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.0021 mg/kg 0.00089 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0012 mg/kg 0.0013 mg/kg 0.002 mg/kg 0.0021 mg/kg 0.0011 mg/kg 0.0023 mg/kg 0.0021 mg/kg 0.0027 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.00086 mg/kg 0.0016 mg/kg 0.0021 mg/kg 24200 mg/kg 99.6 mg/kg 0.798 mg/kg 7.27 mg/kg 26.5 mg/kg 4.72 mg/kg 31.1 mg/kg 187 mg/kg 1890 mg/kg 288 mg/kg 43.7 mg/kg 45.1 mg/kg 5.47 mg/kg 0.244 mg/kg 7.98 mg/kg 0.106 mg/kg 9.56 mg/kg 6.96 mg/kg 0.232 mg/kg 15.6 mg/kg 0.488 mg/kg 0.0891 mg/kg 0.216 mg/kg 7.31 mg/kg 0.0449 mg/kg 22.2 mg/kg 0.000000108 mg/kg 6.64E‐08 mg/kg 0.000000157 mg/kg 0.000000481 mg/kg 0.00000172 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.000000311 mg/kg 0.000000497 mg/kg 0.000000467 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000114 mg/kg Detected Y N Y N N N N N N N N N N N Y Y Y Y Y Y Y Y Y N Y N Y N N N N N N N N N N N N N Y N N N N Y Y Y N Y Y N Y N N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y N N N N Y Y Y N N N N N Project  Qual  Code Validation Note U U U U U U U U U U U U J F F F J U U U U U U U U U U U U U U U J U U U U J J J U J F F F F, Original Result = 1 U U U J J U F B B J U B J U J J J J U U U U J J J U UJ UJ UJ UJ F, B F, B F, B F, B F, B F, B F, B F, B B F, B M, F, B M, F, B M, F, B M, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 1400 No 2.36E‐02 1 Yes 1.00E+01 1400 No 4.50E‐02 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 1.46E‐03 Ecological RBSL 0.0325 No 5.23E‐02 Suburban Residential RBSL 7.29 No 2.33E‐04 Suburban Residential RBSL 53 No 3.21E‐05 Ecological RBSL 1.1 No 1.55E‐03 Ecological RBSL 0.33 No 5.15E‐03 Ecological RBSL 2.2 No 2.64E‐04 Ecological RBSL 0.387 No 8.79E‐03 Suburban Residential RBSL 0.0387 No 9.82E‐02 Suburban Residential RBSL 0.387 No 1.50E‐02 Suburban Residential RBSL 7.4 No 4.19E‐04 Ecological RBSL 0.387 No 6.98E‐03 Suburban Residential RBSL 1.2 No 4.75E‐03 Ecological RBSL 0.113 No 8.23E‐03 Suburban Residential RBSL 54 No 1.20E‐04 Ecological RBSL 0.89 No 1.91E‐03 Ecological RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 14.6 No 1.16E‐04 Suburban Residential RBSL 1.3 No 1.69E‐03 Ecological RBSL 1.2 No 1.42E‐03 Ecological RBSL 1400 No 4.50E‐03 1400 No 4.50E‐03 1400 No 4.50E‐03 1 Yes 6.30E+00 1400 No 9.29E‐03 0.32 No 7.19E‐02 Ecological RBSL 90 No 2.56E‐04 Ecological RBSL 2.3 No 1.00E‐02 Ecological RBSL 4.5 No 5.11E‐03 Ecological RBSL 0.11 No 2.09E‐01 Ecological RBSL 13 No 1.77E‐03 Ecological RBSL 0.0325 No 6.46E‐02 Suburban Residential RBSL 7.29 No 1.22E‐04 Suburban Residential RBSL 53 No 3.96E‐05 Ecological RBSL 1.1 No 1.91E‐03 Ecological RBSL 0.33 No 6.36E‐03 Ecological RBSL 2.2 No 9.55E‐04 Ecological RBSL 0.387 No 3.10E‐03 Suburban Residential RBSL 0.0387 No 3.36E‐02 Suburban Residential RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 7.4 No 2.84E‐04 Ecological RBSL 0.387 No 2.84E‐03 Suburban Residential RBSL 1.2 No 1.92E‐03 Ecological RBSL 0.113 No 1.86E‐02 Suburban Residential RBSL 54 No 5.00E‐05 Ecological RBSL 0.89 No 2.36E‐03 Ecological RBSL 0.387 No 5.43E‐03 Suburban Residential RBSL 14.6 No 5.89E‐05 Suburban Residential RBSL 1.3 No 1.23E‐03 Ecological RBSL 1.2 No 1.75E‐03 Ecological RBSL 37900 No 6.39E‐01 Background 203.8 No 4.89E‐01 Background 4.8 No 1.66E‐01 Ecological RBSL 22 No 3.30E‐01 Ecological RBSL 60.11 No 4.41E‐01 Background 26.18 No 1.80E‐01 Background 64.4 No 4.83E‐01 Background 723 No 2.59E‐01 Background 7524 No 2.51E‐01 Background 754 No 3.82E‐01 Background 111.8 No 3.91E‐01 Background 153 No 2.95E‐01 Background 10.64 No 5.14E‐01 Background 0.5 No 4.88E‐01 MRL 24.2 No 3.30E‐01 Background 0.435 No 2.44E‐01 Background 42 No 2.28E‐01 Background 33.9 No 2.05E‐01 Background 1.642 No 1.41E‐01 Background 64.2 No 2.43E‐01 Background 1 No 4.88E‐01 MRL 0.99 No 9.00E‐02 Ecological RBSL 0.761 No 2.84E‐01 Suburban Residential RBSL 24.2 No 3.02E‐01 Background 0.99 No 4.54E‐02 Ecological RBSL 24.2 No 9.17E‐01 Background 0.0000057 No 1.89E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 2.79E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 10 10 21 19 19 19 19 19 19 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 6.3 6.3 6.3 6.3 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 12.2 0.61 0.305 6.1 0.915 0.61 2.4 0.61 61 61 0.61 2.44 6.1 0.244 0.488 0.122 0.244 0.244 0.122 0.488 0.488 0.122 0.122 0.456 0.106 0.441 mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.2 4.2 8.3 6.2 6.2 6.2 6.2 6.2 6.2 0.69 0.69 0.69 0.69 0.35 0.35 0.69 0.69 0.69 0.69 0.69 0.35 0.69 0.69 0.69 0.69 0.69 0.69 0.69 2.5 2.5 2.5 2.5 5.1 7.6 7.6 7.6 7.6 7.6 7.6 0.85 0.85 0.85 0.85 0.42 0.42 0.85 0.85 0.85 0.85 0.85 0.42 0.85 0.85 0.85 0.85 0.85 0.85 0.85 9.41 0.0403 0.0818 1.01 0.107 0.11 0.67 0.101 16.5 20.4 0.134 0.244 1.01 0.083 0.102 0.0561 0.178 0.0178 0.061 0.188 0.122 0.0244 0.0366 0.0957 0.0277 0.0927 mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 1.14 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0125 0.0278 0.0158 0.0164 0.027 0.0166 0.0284 0.0201 0.0271 0.0187 0.0332 0.0163 0.0181 0.028 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S001 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S002 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:20 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:25 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Page 79 of 108 CAS Number 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 Result  Value 0.0546 1.71 3.38 1.29 1.4 2.74 21.5 1.06 4.04 0.842 0.363 330 330 670 330 670 330 330 330 330 330 330 450 330 2200 2200 330 330 330 18300 120 0.75 7.42 22.1 7.35 18.4 425 3400 128 41.5 47.2 4.36 0.24 6.94 0.249 19.4 9.39 0.746 20.8 0.199 0.035 0.389 5.3 5.3 5.3 5.3 11 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 0.48 1.4 1.1 1.2 1.8 1.8 1.4 1.8 2.7 1.8 1.8 1.8 2.3 2.6 24 0.00168 0.00168 0.0107 6.3 6.3 6.3 6.3 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00000114 mg/kg 0.00000571 mg/kg 0.00000338 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000274 mg/kg 0.0000215 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000114 mg/kg 0.00000114 mg/kg 0.33 mg/kg 0.33 mg/kg 0.67 mg/kg 0.33 mg/kg 0.67 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.45 mg/kg 0.33 mg/kg 2.2 mg/kg 2.2 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 18300 mg/kg 120 mg/kg 0.75 mg/kg 7.42 mg/kg 22.1 mg/kg 7.35 mg/kg 18.4 mg/kg 425 mg/kg 3400 mg/kg 128 mg/kg 41.5 mg/kg 47.2 mg/kg 4.36 mg/kg 0.24 mg/kg 6.94 mg/kg 0.249 mg/kg 19.4 mg/kg 9.39 mg/kg 0.746 mg/kg 20.8 mg/kg 0.199 mg/kg 0.035 mg/kg 0.389 mg/kg 5.3 mg/kg 5.3 mg/kg 5.3 mg/kg 5.3 mg/kg 11 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00048 mg/kg 0.0014 mg/kg 0.0011 mg/kg 0.0012 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0014 mg/kg 0.0018 mg/kg 0.0027 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0023 mg/kg 0.0018 mg/kg 0.024 mg/kg 1.68E‐09 mg/kg 1.68E‐09 mg/kg 1.07E‐08 mg/kg 6.3 mg/kg 6.3 mg/kg 6.3 mg/kg 6.3 mg/kg 13 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg Detected N N Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N Y Y Y Y N N Y N Y N N N Y N Y Y Y Y N N N N N N N N N N N N N N N Project  Qual  Code UJ UJ J UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U Validation Note M, F, B M, F F M, F M, F, B F, B F, B M, F M, F M, F, B M, F B B J J J U U U U U U U U U U U U U U U U J J J J U U J U F F F U U U U J U U U U U U U U U U U U U U U F Q, Q F F F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.59E‐01 Ecological RBSL 0.3 Yes 1.10E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.10E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 4.09E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.10E+00 Ecological RBSL No SL No SL ‐‐ ‐‐ No SL No SL 37900 No 4.83E‐01 Background 203.8 No 5.89E‐01 Background 4.8 No 1.56E‐01 Ecological RBSL 22 No 3.37E‐01 Ecological RBSL 60.11 No 3.68E‐01 Background 26.18 No 2.81E‐01 Background 64.4 No 2.86E‐01 Background 723 No 5.88E‐01 Background 7524 No 4.52E‐01 Background 754 No 1.70E‐01 Background 111.8 No 3.71E‐01 Background 153 No 3.08E‐01 Background 10.64 No 4.10E‐01 Background 0.5 No 4.80E‐01 MRL 24.2 No 2.87E‐01 Background 0.435 No 5.72E‐01 Background 42 No 4.62E‐01 Background 33.9 No 2.77E‐01 Background 1.642 No 4.54E‐01 Background 64.2 No 3.24E‐01 Background 1 No 1.99E‐01 MRL 0.99 No 3.54E‐02 Ecological RBSL 0.761 No 5.11E‐01 Suburban Residential RBSL 1400 No 3.79E‐03 1400 No 3.79E‐03 1400 No 3.79E‐03 1 Yes 5.30E+00 1400 No 7.86E‐03 0.32 No 5.94E‐02 Ecological RBSL 90 No 2.11E‐04 Ecological RBSL 2.3 No 8.26E‐03 Ecological RBSL 4.5 No 4.22E‐03 Ecological RBSL 0.11 No 1.73E‐01 Ecological RBSL 13 No 1.46E‐03 Ecological RBSL 0.0325 No 5.54E‐02 Suburban Residential RBSL 7.29 No 2.47E‐04 Suburban Residential RBSL 53 No 3.40E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 5.45E‐03 Ecological RBSL 2.2 No 2.18E‐04 Ecological RBSL 0.387 No 3.62E‐03 Suburban Residential RBSL 0.0387 No 2.84E‐02 Suburban Residential RBSL 0.387 No 3.10E‐03 Suburban Residential RBSL 7.4 No 2.43E‐04 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 1.2 No 1.17E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 5.00E‐05 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 14.6 No 1.23E‐04 Suburban Residential RBSL 1.3 No 1.77E‐03 Ecological RBSL 1.2 No 1.50E‐03 Ecological RBSL 0.5 No 4.80E‐02 Ecological RBSL 0.0000057 No 2.95E‐04 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 1.90E‐02 Background 1400 No 4.50E‐03 1400 No 4.50E‐03 1400 No 4.50E‐03 1 Yes 6.30E+00 1400 No 9.29E‐03 0.32 No 7.19E‐02 Ecological RBSL 90 No 2.56E‐04 Ecological RBSL 2.3 No 1.00E‐02 Ecological RBSL 4.5 No 5.11E‐03 Ecological RBSL 0.11 No 2.09E‐01 Ecological RBSL 13 No 1.77E‐03 Ecological RBSL 0.0325 No 6.46E‐02 Suburban Residential RBSL 7.29 No 2.88E‐04 Suburban Residential RBSL 53 No 3.96E‐05 Ecological RBSL 1.1 No 1.91E‐03 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 1.14 5.71 5.71 5.71 5.71 11.4 11.4 5.71 5.71 1.14 1.14 330 330 670 330 670 330 330 330 330 330 330 450 330 2200 2200 330 330 330 11.6 0.579 0.29 5.79 0.869 0.579 2.3 0.579 57.9 57.9 0.579 2.32 5.79 0.232 0.463 0.116 0.232 0.232 0.116 0.463 0.463 0.116 0.116 5.3 5.3 5.3 5.3 11 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.3 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.028 0.0139 0.0278 0.0172 0.0275 0.0241 0.0208 0.0185 0.0332 0.028 0.028 110 110 220 110 220 110 110 220 280 170 220 280 110 1700 1700 140 110 170 8.93 0.0382 0.0776 0.961 0.102 0.104 0.64 0.0961 15.6 19.3 0.127 0.232 0.961 0.0787 0.0973 0.0533 0.169 0.0169 0.0579 0.178 0.116 0.0232 0.0347 2.1 2.1 2.1 2.1 4.3 6.4 6.4 6.4 6.4 6.4 6.4 0.71 0.71 0.71 0.71 0.36 0.36 0.71 0.71 0.71 0.71 0.71 0.36 0.71 0.71 0.71 0.71 0.71 0.71 0.71 2.2 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 6.3 6.3 6.3 6.3 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 2.5 2.5 2.5 2.5 5 7.5 7.5 7.5 7.5 7.5 7.5 0.84 0.84 0.84 0.84 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2020 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2020S003 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/17/13 9:30 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 6850 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 Analyte Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl Perchlorate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Page 80 of 108 CAS Number 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 14797730 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 Result  Value 2.1 1.4 3.6 2.9 3.9 1.3 1.5 4.1 2.1 6.9 2.1 1.4 2.1 5.6 7.1 0.315 0.805 0.0961 0.177 0.0699 0.102 0.105 0.117 0.167 0.376 0.314 0.0683 0.262 0.0627 0.103 1.24 1.54 0.878 0.816 1.29 7.41 1.03 2.21 0.339 0.326 340 340 680 340 680 340 340 340 340 340 340 460 340 2300 2300 340 340 340 5 19400 81.8 0.767 5.52 24.9 4.07 29.6 222 1570 115 35.3 47.8 4.4 0.106 7.08 0.0757 11.8 5.61 0.16 17 0.122 0.0973 0.273 20000 145 0.768 6.65 23.9 7.75 19.5 440 3810 120 45 51.1 4.28 0.277 8.08 0.363 20.8 10.8 0.714 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.0021 mg/kg 0.0014 mg/kg 0.0036 mg/kg 0.0029 mg/kg 0.0039 mg/kg 0.0013 mg/kg 0.0015 mg/kg 0.0041 mg/kg 0.0021 mg/kg 0.0069 mg/kg 0.0021 mg/kg 0.0014 mg/kg 0.0021 mg/kg 0.0056 mg/kg 0.0071 mg/kg 0.00000624 mg/kg 0.000000805 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000125 mg/kg 0.00000125 mg/kg 0.00000124 mg/kg 0.00000154 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000129 mg/kg 0.00000741 mg/kg 0.00000624 mg/kg 0.00000624 mg/kg 0.00000125 mg/kg 0.00000125 mg/kg 0.34 mg/kg 0.34 mg/kg 0.68 mg/kg 0.34 mg/kg 0.68 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.46 mg/kg 0.34 mg/kg 2.3 mg/kg 2.3 mg/kg 0.34 mg/kg 0.34 mg/kg 0.34 mg/kg 0.005 mg/kg 19400 mg/kg 81.8 mg/kg 0.767 mg/kg 6.09 mg/kg 24.9 mg/kg 4.07 mg/kg 29.6 mg/kg 222 mg/kg 1570 mg/kg 115 mg/kg 35.3 mg/kg 47.8 mg/kg 4.4 mg/kg 0.244 mg/kg 7.08 mg/kg 0.0757 mg/kg 11.8 mg/kg 5.61 mg/kg 0.16 mg/kg 17 mg/kg 0.487 mg/kg 0.0973 mg/kg 0.273 mg/kg 20000 mg/kg 145 mg/kg 0.768 mg/kg 6.65 mg/kg 23.9 mg/kg 7.75 mg/kg 19.5 mg/kg 440 mg/kg 3810 mg/kg 120 mg/kg 45 mg/kg 51.1 mg/kg 4.28 mg/kg 0.277 mg/kg 8.08 mg/kg 0.363 mg/kg 20.8 mg/kg 10.8 mg/kg 0.714 mg/kg Detected N Y Y Y Y Y Y Y N Y N Y N Y Y N Y N N N N N N N N N N N N N Y Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Project  Qual  Code Validation Note U J J J U U J U U J U U UJ UJ UJ U U UJ UJ UJ U UJ UJ J J UJ UJ J J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U F B, F F, B F, B B, F M, F, B M, F, B M, F, B F, B B M, F, B M, F, B M, F, B F, B M, B M, F, B F F M, F M, F, B F, B F, B M, F M, F M, F, B M, F B U B J U B J U J Q, Q, B J F, B Q, Q J Q Q, Q J J J J J J J Q, Q, Q Q, Q Q, Q Q, Q Q, Q, F Q Boeing Soil Char Level  (mg/kg) 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 6.36E‐03 6.36E‐04 9.30E‐03 7.49E‐02 1.01E‐02 1.76E‐04 3.88E‐03 3.42E‐03 1.86E‐02 1.28E‐04 2.36E‐03 3.62E‐03 1.44E‐04 4.31E‐03 5.92E‐03 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.70E‐01 1.13E+00 No SL No SL No SL No SL 1.13E+00 No SL No SL No SL No SL 4.18E‐03 No SL No SL No SL 1.13E+00 No SL No SL 1.00E‐02 5.12E‐01 4.01E‐01 1.60E‐01 2.77E‐01 4.14E‐01 1.55E‐01 4.60E‐01 3.07E‐01 2.09E‐01 1.53E‐01 3.16E‐01 3.12E‐01 4.14E‐01 4.88E‐01 2.93E‐01 1.74E‐01 2.81E‐01 1.65E‐01 9.74E‐02 2.65E‐01 4.87E‐01 9.83E‐02 3.59E‐01 5.28E‐01 7.11E‐01 1.60E‐01 3.02E‐01 3.98E‐01 2.96E‐01 3.03E‐01 6.09E‐01 5.06E‐01 1.59E‐01 4.03E‐01 3.34E‐01 4.02E‐01 5.54E‐01 3.34E‐01 8.34E‐01 4.95E‐01 3.19E‐01 4.35E‐01 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 6.24 6.24 6.24 6.24 6.24 6.24 6.24 6.24 6.24 6.24 6.24 6.24 6.24 1.25 1.25 6.24 6.24 6.24 6.24 12.5 12.5 6.24 6.24 1.25 1.25 340 340 680 340 680 340 340 340 340 340 340 460 340 2300 2300 340 340 340 5 12.2 0.609 0.305 6.09 0.914 0.609 2.4 0.609 60.9 60.9 0.609 2.44 6.09 0.244 0.487 0.122 0.244 0.244 0.122 0.487 0.487 0.122 0.122 10.9 0.545 0.272 5.45 0.817 0.545 2.2 0.545 54.5 54.5 0.545 2.18 5.45 0.218 0.436 0.109 0.218 0.218 0.109 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.42 0.42 0.84 0.84 0.84 0.84 0.84 0.42 0.84 0.84 0.84 0.84 0.84 0.84 0.84 0.0154 0.0351 0.021 0.0197 0.0292 0.0191 0.0317 0.0226 0.0302 0.0257 0.0448 0.0182 0.0245 0.0356 0.0359 0.0177 0.0351 0.0198 0.0304 0.0325 0.0236 0.0251 0.0448 0.0356 0.0359 110 110 230 110 230 110 110 230 290 170 230 290 110 1700 1700 280 110 170 2.6 9.39 0.0402 0.0816 1.01 0.107 0.11 0.67 0.101 16.4 20.3 0.134 0.244 1.01 0.0828 0.102 0.056 0.178 0.0178 0.0609 0.188 0.122 0.0244 0.0365 8.4 0.0359 0.073 0.904 0.0959 0.098 0.6 0.0904 14.7 18.2 0.12 0.218 0.904 0.0741 0.0915 0.0501 0.159 0.0159 0.0545 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S001 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S002 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:35 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 10:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 6020 6020 6020 6020 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8015B 8015B 8015B 8015B 8015B 8260B 8260B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte Nickel Selenium Silver Thallium C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Xylenes, Total C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) 1,2,4‐Trichlorobenzene Hexachlorobutadiene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Page 81 of 108 CAS Number 7440020 7782492 7440224 7440280 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 1330207 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 120821 87683 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 630206 71556 79345 76131 79005 75343 75354 563586 87616 96184 95636 96128 106934 95501 107062 78875 108678 541731 142289 106467 75887 110758 591786 108101 67641 71432 108861 74975 75274 75252 74839 56235 108907 75003 Result  Value 23.2 0.17 0.039 0.419 6.4 6.4 6.4 6.4 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 1.8 2.1 2.1 5 5.2 5.2 5.2 5.2 10 5 5 19 19 19 19 19 19 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 11 11 22 5 5 5 5 5 5 5 5 5 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 23.2 0.17 0.039 0.419 6.4 6.4 6.4 6.4 13 0.023 0.023 0.023 0.023 0.023 0.023 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0021 0.0018 0.0021 0.0021 0.005 5.2 5.2 5.2 5.2 10 0.005 0.005 0.019 0.019 0.019 0.019 0.019 0.019 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.0017 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.011 0.011 0.011 0.022 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.005 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N J J J J U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note Q Q Q Q, Q F F L L F F L L, L Boeing Soil Char Level  (mg/kg) 64.2 1 0.99 0.761 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 3.4 1400 1400 1400 1 1400 10 0.022 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 2.87 2460 0.288 220 0.533 1.89 6.9 ‐‐ 10 ‐‐ 3.1 0.0978 0.104 130 0.261 0.439 3.2 23 ‐‐ 1.33 ‐‐ 0.01 23 4.5 46 0.115 25 ‐‐ 0.195 23 3.2 0.071 21 ‐‐ Exceeds Boeing Soil Char Level No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No No SL No No No No No No No No No SL No No SL Yes No No No No No No SL No No No No No No SL Ratio Boeing Soil Char Level 3.61E‐01 1.70E‐01 3.94E‐02 5.51E‐01 4.57E‐03 4.57E‐03 4.57E‐03 6.40E+00 9.29E‐03 7.19E‐02 2.56E‐04 1.00E‐02 5.11E‐03 2.09E‐01 1.77E‐03 6.46E‐02 2.88E‐04 3.96E‐05 1.91E‐03 6.36E‐03 9.55E‐04 5.43E‐03 5.43E‐02 5.43E‐03 2.84E‐04 5.43E‐03 1.75E‐03 1.86E‐02 3.89E‐05 2.36E‐03 5.43E‐03 1.23E‐04 1.62E‐03 1.75E‐03 1.47E‐03 3.71E‐03 3.71E‐03 3.71E‐03 5.20E+00 7.14E‐03 5.00E‐04 2.27E‐01 5.94E‐02 2.11E‐04 8.26E‐03 4.22E‐03 1.73E‐01 1.46E‐03 5.23E‐02 2.33E‐04 3.21E‐05 1.55E‐03 5.15E‐03 7.73E‐04 4.39E‐03 4.39E‐02 4.39E‐03 2.30E‐04 4.39E‐03 1.42E‐03 1.50E‐02 3.15E‐05 1.91E‐03 4.39E‐03 1.16E‐04 1.31E‐03 1.42E‐03 1.74E‐03 2.03E‐06 1.74E‐02 2.27E‐05 9.38E‐03 2.65E‐03 7.25E‐04 No SL 5.00E‐04 No SL 1.61E‐03 5.11E‐02 4.81E‐02 3.85E‐05 1.92E‐02 1.14E‐02 1.56E‐03 2.17E‐04 No SL 3.76E‐03 No SL 1.10E+00 4.78E‐04 2.44E‐03 4.78E‐04 4.35E‐02 2.00E‐04 No SL 2.56E‐02 2.17E‐04 1.56E‐03 7.04E‐02 2.38E‐04 No SL SCL Basis Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 0.436 0.436 0.109 0.109 6.4 6.4 6.4 6.4 13 23 23 23 23 23 23 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 5 5.2 5.2 5.2 5.2 10 5 5 19 19 19 19 19 19 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 1.7 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 11 11 11 22 5 5 5 5 5 5 5 5 5 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.168 0.109 0.0218 0.0327 2.6 2.6 2.6 2.6 5.1 7.6 7.6 7.6 7.6 7.6 7.6 0.85 0.85 0.85 0.85 0.42 0.42 0.85 0.85 0.85 0.85 0.85 0.42 0.85 0.85 0.85 0.85 0.85 0.85 0.85 1 2.1 2.1 2.1 2.1 4.2 1 2 6.2 6.2 6.2 6.2 6.2 6.2 0.69 0.69 0.69 0.69 0.34 0.34 0.69 0.69 0.69 0.69 0.69 0.34 0.69 0.69 0.69 0.69 0.69 0.69 0.69 1 1 1 2 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 2 2 3 3 8 0.5 1 1 1 1 2 1 1 2 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2021 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2021S003 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 11:40 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A Analyte Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethylbenzene Cumene Methyl ethyl ketone Methyl tert‐butyl ether Methylene chloride m‐Xylene & p‐Xylene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane Styrene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN Page 82 of 108 CAS Number 67663 74873 79389 156592 10061015 124481 74953 75718 108203 100414 98828 78933 1634044 75092 179601231 104518 103651 95498 95476 106434 99876 135988 594207 100425 994058 75650 637923 98066 127184 108883 156605 10061026 79016 75694 75014 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 Result  Value 5 5 5 5 5 5 5 5 5 5 5 11 5 5 5 5 5 5 5 5 5 5 5 5 5 54 5 5 5 5 5 5 5 5 5 13300 109 0.478 4.24 25.1 5.93 31.7 293 1980 119 44.6 55 3.65 0.204 6.32 0.118 10.9 4.36 0.229 19.1 0.103 0.0299 0.257 0.0972 0.0467 0.236 1.08 11.2 0.109 0.122 0.211 0.1 0.472 0.29 0.561 0.505 0.123 0.0941 0.104 0.0974 0.0325 2.89 24.3 1.74 3.47 3.22 188 1.92 4.96 2.52 0.232 270 270 550 270 550 270 270 270 270 270 270 370 270 1800 1800 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.011 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.054 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 0.005 mg/kg 13300 mg/kg 109 mg/kg 0.478 mg/kg 5.15 mg/kg 25.1 mg/kg 5.93 mg/kg 31.7 mg/kg 293 mg/kg 1980 mg/kg 119 mg/kg 44.6 mg/kg 55 mg/kg 3.65 mg/kg 0.206 mg/kg 6.32 mg/kg 0.118 mg/kg 10.9 mg/kg 4.36 mg/kg 0.229 mg/kg 19.1 mg/kg 0.412 mg/kg 0.0299 mg/kg 0.257 mg/kg 9.72E‐08 mg/kg 4.67E‐08 mg/kg 0.000000236 mg/kg 0.00000108 mg/kg 0.0000112 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.000000561 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.000000973 mg/kg 0.000000973 mg/kg 0.00000486 mg/kg 0.0000243 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.00000322 mg/kg 0.000188 mg/kg 0.00000486 mg/kg 0.00000486 mg/kg 0.000000973 mg/kg 0.000000973 mg/kg 0.27 mg/kg 0.27 mg/kg 0.55 mg/kg 0.27 mg/kg 0.55 mg/kg 0.27 mg/kg 0.27 mg/kg 0.27 mg/kg 0.27 mg/kg 0.27 mg/kg 0.27 mg/kg 0.37 mg/kg 0.27 mg/kg 1.8 mg/kg 1.8 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y Y Y N N N N N N Y N N N N N N N Y N N Y Y N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Q, Q, B U J F, B Q, Q J Q Q, Q J U J J J J J J U J J Q, Q, Q, B Q, Q Q, Q Q, Q Q, Q, F Q Q Q Q Q, Q J J U U U U UJ U J U U UJ U U UJ UJ UJ UJ J J UJ UJ UJ UJ U U U U U U U U U U U U U U U F, B E, F, B F, B F, B B B M, F, B F F, B F, B F, B M, F, B F, B B M, F, B E, M, F, B F, B M, F, B E, M, F, B F, B E, F, B M, F, B M, F, B E, M, B M, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.733 No 6.82E‐03 Suburban Residential RBSL 3.2 No 1.56E‐03 Ecological RBSL ‐‐ No SL No SL 9.22 No 5.42E‐04 Suburban Residential RBSL ‐‐ No SL No SL 7.28 No 6.87E‐04 Suburban Residential RBSL 22.3 No 2.24E‐04 Suburban Residential RBSL 41 No 1.22E‐04 Ecological RBSL ‐‐ No SL No SL 2.31 No 2.16E‐03 Suburban Residential RBSL 1.3 No 3.85E‐03 Ecological RBSL 8160 No 1.35E‐06 Ecological RBSL ‐‐ No SL No SL 2.97 No 1.68E‐03 Suburban Residential RBSL 3.3 No 1.52E‐03 Ecological RBSL 61 No 8.20E‐05 Ecological RBSL 73 No 6.85E‐05 Ecological RBSL 16 No 3.13E‐04 Ecological RBSL 3.4 No 1.47E‐03 Ecological RBSL 16 No 3.13E‐04 Ecological RBSL 3.7 No 1.35E‐03 Ecological RBSL 0.98 No 5.10E‐03 Ecological RBSL ‐‐ No SL No SL 210 No 2.38E‐05 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 1.1 No 4.55E‐03 Ecological RBSL 0.416 No 1.20E‐02 Suburban Residential RBSL 59 No 8.47E‐05 Ecological RBSL 85.3 No 5.86E‐05 Suburban Residential RBSL ‐‐ No SL No SL 0.797 No 6.27E‐03 Suburban Residential RBSL 170 No 2.94E‐05 Ecological RBSL 0.0204 No 2.45E‐01 Suburban Residential RBSL 37900 No 3.51E‐01 Background 203.8 No 5.35E‐01 Background 4.8 No 9.96E‐02 Ecological RBSL 22 No 2.34E‐01 Ecological RBSL 60.11 No 4.18E‐01 Background 26.18 No 2.27E‐01 Background 64.4 No 4.92E‐01 Background 723 No 4.05E‐01 Background 7524 No 2.63E‐01 Background 754 No 1.58E‐01 Background 111.8 No 3.99E‐01 Background 153 No 3.59E‐01 Background 10.64 No 3.43E‐01 Background 0.5 No 4.12E‐01 MRL 24.2 No 2.61E‐01 Background 0.435 No 2.71E‐01 Background 42 No 2.60E‐01 Background 33.9 No 1.29E‐01 Background 1.642 No 1.39E‐01 Background 64.2 No 2.98E‐01 Background 1 No 4.12E‐01 MRL 0.99 No 3.02E‐02 Ecological RBSL 0.761 No 3.38E‐01 Suburban Residential RBSL 0.0000057 No 1.71E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 4.19E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 2.93E‐01 Ecological RBSL 0.3 No 9.00E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 No 9.00E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 3.36E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 5 5 5 5 5 5 5 5 5 5 5 11 5 5 5 5 5 5 5 5 5 5 5 5 5 54 5 5 5 5 5 5 5 5 5 10.3 0.515 0.258 5.15 0.773 0.515 2.1 0.515 51.5 51.5 0.515 2.06 5.15 0.206 0.412 0.103 0.206 0.206 0.103 0.412 0.412 0.103 0.103 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1 2 2 1 1 1 1 2 1 1 1 4 0.5 2 1 1 1 1 1 1 1 1 1 1 1 22 1 1 1 1 1 1 1 2 1 7.95 0.034 0.0691 0.856 0.0907 0.0928 0.57 0.0856 13.9 17.2 0.113 0.206 0.856 0.0701 0.0866 0.0474 0.151 0.0151 0.0515 0.159 0.103 0.0206 0.0309 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 4.86 4.86 4.86 4.86 4.86 4.86 4.86 4.86 4.86 4.86 4.86 4.86 4.86 0.973 0.973 4.86 4.86 4.86 4.86 9.73 9.73 4.86 4.86 0.973 0.973 270 270 550 270 550 270 270 270 270 270 270 370 270 1800 1800 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.012 0.0408 0.0139 0.0177 0.0319 0.0179 0.0339 0.018 0.0322 0.0219 0.0338 0.0164 0.0192 0.0339 0.0211 0.0128 0.0408 0.0175 0.0327 0.02 0.0274 0.0205 0.0338 0.0339 0.0211 92 92 180 92 180 92 92 180 230 140 180 230 92 1400 1400 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N Y N N Y N N N N Y N Y Y Y Y N Y N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022D001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:10 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Page 83 of 108 CAS Number 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 Result  Value 270 270 270 1.7 1.7 36 17 90 12 17 24 2500 2500 0.1 4.4 0.67 3.9 0.4 0.19 18.3 0.18 20900 189 0.811 6.17 22.9 12.7 22.5 887 2800 212 50 54.5 4.83 0.202 8.14 0.288 14.8 12 0.684 21.3 0.14 0.0622 0.378 17 17 17 17 17 17 17 45 17 17 17 17 8.3 8.3 10 170 8.3 17 17 8.3 17 17 17 18 8.3 8.3 8.3 17 67 330 1.29 1.49 3.26 9.43 121 0.717 0.949 1.23 0.525 4.06 0.524 2.84 1.97 0.736 0.579 0.885 0.794 0.0788 28.2 285 14.6 26.5 33.6 2880 10.7 6.17 12.5 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.27 mg/kg 0.27 mg/kg 0.27 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.036 mg/kg 0.017 mg/kg 0.09 mg/kg 0.012 mg/kg 0.017 mg/kg 0.024 mg/kg 2.5 mg/kg 2.5 mg/kg 2 mg/kg 4.4 mg/kg 0.67 mg/kg 3.9 mg/kg 1 mg/kg 0.19 mg/kg 18.3 mg/kg 0.5 mg/kg 20900 mg/kg 189 mg/kg 0.811 mg/kg 6.17 mg/kg 22.9 mg/kg 12.7 mg/kg 22.5 mg/kg 887 mg/kg 2800 mg/kg 212 mg/kg 50 mg/kg 54.5 mg/kg 4.83 mg/kg 0.198 mg/kg 8.14 mg/kg 0.288 mg/kg 14.8 mg/kg 12 mg/kg 0.684 mg/kg 21.3 mg/kg 0.14 mg/kg 0.0622 mg/kg 0.378 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.045 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.0083 mg/kg 0.0083 mg/kg 0.01 mg/kg 0.17 mg/kg 0.0083 mg/kg 0.017 mg/kg 0.017 mg/kg 0.0083 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.018 mg/kg 0.0083 mg/kg 0.0083 mg/kg 0.0083 mg/kg 0.017 mg/kg 0.067 mg/kg 0.33 mg/kg 0.00000129 mg/kg 0.00000149 mg/kg 0.00000326 mg/kg 0.00000943 mg/kg 0.000121 mg/kg 0.00000514 mg/kg 0.000000949 mg/kg 0.00000123 mg/kg 0.00000514 mg/kg 0.00000406 mg/kg 0.000000524 mg/kg 0.00000284 mg/kg 0.00000197 mg/kg 0.00000514 mg/kg 0.000000579 mg/kg 0.00000514 mg/kg 0.00000103 mg/kg 0.00000103 mg/kg 0.00000514 mg/kg 0.000285 mg/kg 0.00000514 mg/kg 0.0000265 mg/kg 0.0000336 mg/kg 0.00288 mg/kg 0.00000514 mg/kg 0.00000514 mg/kg 0.00000103 mg/kg Detected N N N N N N N N N N N N N N Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y N Y Y N Y Y Y Y N Y N N N N Y N Y Y Y N N N Project  Qual  Code U U U U U U U U U U UJ U U U J J J U J Validation Note L L L Q Q F U Q, Q, B J J F, B Q, Q E J J E, Q Q, Q J U J J J J J J J J J U U U U U U U Q, Q, Q, B Q, Q Q, Q Q, Q Q, Q, F Q Q Q Q Q, Q U U U U U U U U U U U U U U U U U U U U U U J UJ J J U J J J J U J U UJ UJ UJ UJ J J UJ UJ UJ F, B E, Q, F, B M, F, B F, B B B F, B F F, B F, B F, B F, B F, B M, B M, F, B E, M, F, B F, B M, F, B E, F, B F, B E, Q, Q, F, B M, F, B M, F, B E, M, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.3 No 9.00E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.8 No 3.54E‐04 Ecological RBSL 0.55 No 3.09E‐03 Ecological RBSL 1.1 No 3.27E‐02 Ecological RBSL 6.2 No 2.74E‐03 Ecological RBSL 39 No 2.31E‐03 Ecological RBSL 14 No 8.57E‐04 Ecological RBSL 0.79 No 2.15E‐02 Ecological RBSL 0.18 No 1.33E‐01 Ecological RBSL 3.3 No 7.58E‐01 MRL 3.3 No 7.58E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 1.91E‐02 Ecological RBSL 2340 No 1.67E‐03 Ecological RBSL ‐‐ No SL No SL 863.2 No 2.20E‐04 Background ‐‐ No SL No SL 0.5 No 1.00E+00 MRL 37900 No 5.51E‐01 Background 203.8 No 9.27E‐01 Background 4.8 No 1.69E‐01 Ecological RBSL 22 No 2.80E‐01 Ecological RBSL 60.11 No 3.81E‐01 Background 26.18 No 4.85E‐01 Background 64.4 No 3.49E‐01 Background 723 Yes 1.23E+00 Background 7524 No 3.72E‐01 Background 754 No 2.81E‐01 Background 111.8 No 4.47E‐01 Background 153 No 3.56E‐01 Background 10.64 No 4.54E‐01 Background 0.5 No 3.96E‐01 MRL 24.2 No 3.36E‐01 Background 0.435 No 6.62E‐01 Background 42 No 3.52E‐01 Background 33.9 No 3.54E‐01 Background 1.642 No 4.17E‐01 Background 64.2 No 3.32E‐01 Background 1 No 1.40E‐01 MRL 0.99 No 6.28E‐02 Ecological RBSL 0.761 No 4.97E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.42E‐01 Ecological RBSL 0.18 No 9.44E‐02 Ecological RBSL 0.082 No 2.07E‐01 Ecological RBSL 0.043 No 3.95E‐01 Ecological RBSL 0.017 No 1.00E+00 MRL 0.039 Yes 1.15E+00 Ecological RBSL 0.025 No 6.80E‐01 Ecological RBSL 0.0051 Yes 3.33E+00 Ecological RBSL 0.004164 Yes 4.08E+00 Background 0.006101 Yes 2.79E+00 Background 0.0348 No 2.39E‐01 Suburban Residential RBSL 0.073 No 1.14E‐01 Ecological RBSL 0.394 No 2.54E‐02 Suburban Residential RBSL 1.1 No 1.55E‐01 Ecological RBSL 0.067 No 1.24E‐01 Ecological RBSL 0.013 Yes 1.31E+00 Ecological RBSL 0.23 No 7.39E‐02 Ecological RBSL 0.22 No 3.77E‐02 Ecological RBSL 0.22 No 7.73E‐02 Ecological RBSL 0.0079 Yes 2.15E+00 Ecological RBSL 0.0092 Yes 1.85E+00 Ecological RBSL 0.0086 Yes 2.09E+00 Ecological RBSL 0.075 No 1.11E‐01 Ecological RBSL 0.087 No 9.54E‐02 Ecological RBSL 0.0017 Yes 4.88E+00 MRL 0.0328 No 5.18E‐01 Suburban Residential RBSL 2.5 No 2.68E‐02 Ecological RBSL 0.493 No 6.69E‐01 Suburban Residential RBSL 0.0000057 No 2.26E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 5.79E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 270 270 270 1.7 1.7 36 17 90 12 17 24 2500 2500 2 5 1 4.4 1 5 5 0.5 9.88 0.494 0.247 4.94 0.741 0.494 2 0.988 49.4 49.4 0.494 1.98 4.94 0.198 0.395 0.0988 0.198 0.198 0.0988 0.395 0.395 0.0988 0.0988 17 17 17 17 17 17 17 17 17 17 17 17 8.3 8.3 10 170 8.3 17 17 8.3 17 17 17 18 8.3 8.3 8.3 17 67 330 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 110 92 140 0.82 0.75 12 6.2 44 4 9 9 760 750 0.1 1 0.4 1.8 0.4 0.1 1.6 0.18 7.62 0.0326 0.0662 0.82 0.0869 0.0889 0.54 0.164 13.3 16.5 0.109 0.198 0.82 0.0672 0.083 0.0454 0.144 0.0144 0.0494 0.152 0.0988 0.0198 0.0296 3.3 3.3 3.6 4.6 8.1 3.3 3.3 3.3 4.9 3.3 5.6 17 3.3 1.7 3 40 1.8 3.3 3.3 2.2 3.3 3.3 3.3 3.3 1.7 3 1.9 3.3 17 110 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 5.14 1.03 1.03 5.14 5.14 5.14 5.14 10.3 10.3 5.14 5.14 1.03 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0386 0.103 0.0456 0.0345 0.0482 0.0337 0.0486 0.0425 0.0488 0.0407 0.0494 0.0351 0.0363 0.059 0.0259 0.0418 0.103 0.0361 0.0485 0.0977 0.114 0.0384 0.0494 0.059 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y N N N N N N N N N Y N N N Y Y Y N Y Y Y Y N N Y N Y N Y Y Y Y N Y N Y Y N N N N N N N N N Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y N Y Y N Y Y Y Y N Y N N N N Y N Y Y Y N N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S001 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:20 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Analysis  Method 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 9012B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Cyanides Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Page 84 of 108 CAS Number 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 24959679 16887006 16984488 NO3 NO2 14265442 14808798 57125 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 Result  Value 0.526 290 290 590 290 590 290 290 290 290 290 290 390 290 2000 2000 290 290 290 1.7 1.7 37 17 91 12 17 24 2500 2500 0.1 9 0.74 19 0.41 0.4 22.6 0.18 16300 117 0.553 7.2 19.8 6.47 17.2 330 3080 227 49.6 90.6 4.57 0.167 7.03 0.279 14 9.25 0.692 18.2 0.165 0.0485 0.232 17 17 17 17 17 17 17 75 17 18 18 19 8.6 8.6 10 180 8.6 18 18 8.6 18 18 18 19 8.6 8.6 8.6 4.7 69 340 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 Result  Value  Units ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00000103 mg/kg 0.29 mg/kg 0.29 mg/kg 0.59 mg/kg 0.29 mg/kg 0.59 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.39 mg/kg 0.29 mg/kg 2 mg/kg 2 mg/kg 0.29 mg/kg 0.29 mg/kg 0.29 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.037 mg/kg 0.017 mg/kg 0.091 mg/kg 0.012 mg/kg 0.017 mg/kg 0.024 mg/kg 2.5 mg/kg 2.5 mg/kg 2.1 mg/kg 9 mg/kg 0.74 mg/kg 19 mg/kg 1 mg/kg 0.4 mg/kg 22.6 mg/kg 0.51 mg/kg 16300 mg/kg 117 mg/kg 0.553 mg/kg 7.2 mg/kg 19.8 mg/kg 6.47 mg/kg 17.2 mg/kg 330 mg/kg 3080 mg/kg 227 mg/kg 49.6 mg/kg 90.6 mg/kg 4.57 mg/kg 0.202 mg/kg 7.03 mg/kg 0.279 mg/kg 14 mg/kg 9.25 mg/kg 0.692 mg/kg 18.2 mg/kg 0.165 mg/kg 0.0485 mg/kg 0.232 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.017 mg/kg 0.075 mg/kg 0.017 mg/kg 0.018 mg/kg 0.018 mg/kg 0.019 mg/kg 0.0086 mg/kg 0.0086 mg/kg 0.01 mg/kg 0.18 mg/kg 0.0086 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0086 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.019 mg/kg 0.0086 mg/kg 0.0086 mg/kg 0.0086 mg/kg 0.0047 mg/kg 0.069 mg/kg 0.34 mg/kg 5.5 mg/kg 5.5 mg/kg 5.5 mg/kg 5.5 mg/kg 11 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N N N N N N Y N N N Y N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N Project  Qual  Code UJ U U U U U U U U U U U U U U U U U U U U U U U U U UJ U U U J J U J Validation Note M, F, B L Q, Q, L Q, Q, L Q, Q Q, Q F U Q, Q, B J J F, B Q, Q E J J E, Q Q, Q J U J J J J J J J J J U U U U U U U U U U J U U U U U UJ U U U U U U U U U J U U U U U U U U U U U U U Q, Q, Q, B Q, Q Q, Q Q, Q Q, Q, F Q Q Q Q Q, Q Q, Q Q, Q F F Boeing Soil Char Level  (mg/kg) ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 4.8 0.55 1.1 6.2 39 14 0.79 0.18 3.3 3.3 ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 0.0051 0.004164 0.006101 0.0348 0.073 0.394 1.1 0.067 0.013 0.23 0.22 0.22 0.0079 0.0092 0.0086 0.075 0.087 0.0017 0.0328 2.5 0.493 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 Exceeds Boeing Soil Char Level No SL No No No SL No SL No SL No SL No No SL No SL No SL No SL No No SL No SL No SL No No SL No SL No No No No No No No No No No No SL No SL No No No SL No No SL Yes No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No No Yes No Yes Yes Yes No No No No No Yes No No No Yes Yes Yes No No Yes No No No No No No Yes No No No No No No No Ratio Boeing Soil Char Level No SL 3.15E‐01 9.67E‐01 No SL No SL No SL No SL 9.67E‐01 No SL No SL No SL No SL 3.55E‐03 No SL No SL No SL 9.67E‐01 No SL No SL 3.54E‐04 3.09E‐03 3.36E‐02 2.74E‐03 2.33E‐03 8.57E‐04 2.15E‐02 1.33E‐01 7.58E‐01 7.58E‐01 No SL No SL 2.11E‐02 8.12E‐03 No SL 4.63E‐04 No SL 1.02E+00 4.30E‐01 5.74E‐01 1.15E‐01 3.27E‐01 3.29E‐01 2.47E‐01 2.67E‐01 4.56E‐01 4.09E‐01 3.01E‐01 4.44E‐01 5.92E‐01 4.30E‐01 4.04E‐01 2.90E‐01 6.41E‐01 3.33E‐01 2.73E‐01 4.21E‐01 2.83E‐01 1.65E‐01 4.90E‐02 3.05E‐01 No SL No SL 1.42E‐01 9.44E‐02 2.07E‐01 3.95E‐01 1.00E+00 1.92E+00 6.80E‐01 3.53E+00 4.32E+00 3.11E+00 2.47E‐01 1.18E‐01 2.54E‐02 1.64E‐01 1.28E‐01 1.38E+00 7.83E‐02 3.91E‐02 8.18E‐02 2.28E+00 1.96E+00 2.21E+00 1.15E‐01 9.89E‐02 5.06E+00 1.43E‐01 2.76E‐02 6.90E‐01 3.93E‐03 3.93E‐03 3.93E‐03 5.50E+00 7.86E‐03 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 SCL Basis Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Background MRL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 1.03 290 290 590 290 590 290 290 290 290 290 290 390 290 2000 2000 290 290 290 1.7 1.7 37 17 91 12 17 24 2500 2500 2.1 5.1 1 4.4 1 5.1 5.1 0.51 10.1 0.506 0.253 5.06 0.759 0.506 2 0.506 50.6 50.6 0.506 2.02 5.06 0.202 0.405 0.101 0.202 0.202 0.101 0.405 0.405 0.101 0.101 17 17 17 17 17 17 17 17 17 18 18 18 8.6 8.6 10 180 8.6 18 18 8.6 18 18 18 19 8.6 8.6 8.6 18 69 340 5.5 5.5 5.5 5.5 11 20 20 20 20 20 20 RL Units MDL ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0259 98 98 200 98 200 98 98 200 250 150 200 250 98 1500 1500 120 98 150 0.83 0.76 12 6.3 45 4.1 9.1 9.1 770 760 0.1 1 0.41 1.8 0.41 0.1 1.6 0.18 7.8 0.0334 0.0678 0.84 0.089 0.0911 0.56 0.084 13.7 16.9 0.111 0.202 0.84 0.0688 0.085 0.0465 0.148 0.0148 0.0506 0.156 0.101 0.0202 0.0304 3.4 3.4 3.7 4.7 8.2 3.4 3.4 3.4 5 3.4 6.5 3.4 3.4 1.8 3.1 41 1.9 5 3.4 2.3 3.4 3.4 3.4 3.4 1.8 3.1 2.3 3.4 18 110 2.2 2.2 2.2 2.2 4.4 6.5 6.5 6.5 6.5 6.5 6.5 MDL  Units ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N Y Y N Y N Y Y Y Y Y Y Y Y Y N Y Y Y N N N Y N N N N Y Y N Y N Y N N N N Y N Y N N Y Y Y Y Y Y Y Y Y N N Y N N Y N N N N N N N N N N N N Y N N Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S002 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2022S003 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S001 ELBS2023S002 ELBS2023S002 ELBS2023S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:30 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/18/13 8:40 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:50 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3.5 3.5 3.5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 4 4 4 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Metals VOCs Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 7199 8315A 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B Analyte n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate Hexavalent Chromium Formaldehyde C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Page 85 of 108 CAS Number 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 18540299 50000 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 Result  Value 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 3.9 0.41 2.1 5.9 5.9 11 5.9 49 210 210 210 210 210 210 19 19 12 19 19 19 19 19 19 19 19 3.9 19 19 19 19 19 19 19 19000 76.3 0.653 6.03 21 4.09 25.4 158 1380 150 38.3 37 4.34 0.223 6.5 0.1 11.6 6.17 0.199 13 0.116 0.0635 0.223 20600 111 0.717 4.47 25.6 6.83 22.5 329 3810 97.3 46.6 58.6 5.07 0.098 5.59 0.189 13.2 10.6 0.443 17 0.175 0.0449 0.296 29300 158 1.2 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0039 0.46 2.1 5.9 5.9 11 5.9 49 0.21 0.21 0.21 0.21 0.21 0.21 0.019 0.019 0.012 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.0039 0.019 0.019 0.019 0.019 0.019 0.019 0.019 19000 76.3 0.653 5.82 21 4.09 25.4 158 1380 150 38.3 37 4.34 0.233 6.5 0.1 11.6 6.17 0.199 13 0.466 0.0635 0.223 20600 111 0.717 4.47 25.6 6.83 22.5 329 3810 97.3 46.6 58.6 5.07 0.228 5.59 0.189 13.2 10.6 0.443 17 0.175 0.0449 0.296 29300 158 1.2 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N N N N N N N N N N N N N N N N Y N N N N Y N Y N N N N N N N N Y N N N N N N N N Y N N N N N N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Project  Qual  Code U U U U U U U U U U U U U U U U U U U J U U U U Validation Note L B U U U U U U U U U J U U U U U U U U J U U U U U U U F F L Q, Q, B U J F, B Q, Q J Q Q, Q J U J J J J J J U J J Q, Q, Q, B Q, Q Q, Q Q, Q Q, Q, F Q Q Q Q Q, Q Q, Q J B J Q, Q Q J UJ Q, Q Q, Q J J Q, Q, B Q, Q J J J Q, Q Q, Q Boeing Soil Char Level  (mg/kg) 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 0.5 1.29 43 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 1.50E‐03 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 7.80E‐03 3.57E‐01 4.88E‐02 4.21E‐03 4.21E‐03 7.86E‐03 5.90E+00 3.50E‐02 6.56E‐01 2.33E‐03 9.13E‐02 4.67E‐02 1.91E+00 1.62E‐02 5.85E‐01 2.61E‐03 2.26E‐04 1.73E‐02 5.76E‐02 8.64E‐03 4.91E‐02 4.91E‐01 4.91E‐02 2.57E‐03 4.91E‐02 3.25E‐03 1.68E‐01 3.52E‐04 2.13E‐02 4.91E‐02 1.30E‐03 1.46E‐02 1.58E‐02 5.01E‐01 3.74E‐01 1.36E‐01 2.65E‐01 3.49E‐01 1.56E‐01 3.94E‐01 2.19E‐01 1.83E‐01 1.99E‐01 3.43E‐01 2.42E‐01 4.08E‐01 4.66E‐01 2.69E‐01 2.30E‐01 2.76E‐01 1.82E‐01 1.21E‐01 2.02E‐01 4.66E‐01 6.41E‐02 2.93E‐01 5.44E‐01 5.45E‐01 1.49E‐01 2.03E‐01 4.26E‐01 2.61E‐01 3.49E‐01 4.55E‐01 5.06E‐01 1.29E‐01 4.17E‐01 3.83E‐01 4.77E‐01 4.56E‐01 2.31E‐01 4.34E‐01 3.14E‐01 3.13E‐01 2.70E‐01 2.65E‐01 1.75E‐01 4.54E‐02 3.89E‐01 7.73E‐01 7.75E‐01 2.50E‐01 SCL Basis Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 4.4 0.46 2.1 5.9 5.9 5.9 5.9 12 210 210 210 210 210 210 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 11.6 0.582 0.291 5.82 0.873 0.582 2.3 0.582 58.2 58.2 0.582 2.33 5.82 0.233 0.466 0.116 0.233 0.233 0.116 0.466 0.466 0.116 0.116 11.4 0.57 0.285 5.7 0.855 0.57 2.3 0.57 57 57 0.57 2.28 5.7 0.228 0.456 0.114 0.228 0.228 0.114 0.456 0.456 0.114 0.114 13 0.651 0.326 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.73 0.73 0.73 0.73 0.36 0.36 0.73 0.73 0.73 0.73 0.73 0.36 0.73 0.73 0.73 0.73 0.73 0.73 0.73 2.3 0.16 1.3 2.4 2.4 2.4 2.4 4.7 70 70 70 70 70 70 7.8 7.8 7.8 7.8 3.9 3.9 7.8 7.8 7.8 7.8 7.8 3.9 7.8 7.8 7.8 7.8 7.8 7.8 7.8 8.98 0.0384 0.078 0.966 0.102 0.105 0.64 0.0966 15.7 19.4 0.128 0.233 0.966 0.0792 0.0978 0.0536 0.17 0.017 0.0582 0.179 0.116 0.0233 0.0349 8.22 0.0376 0.0763 0.957 0.182 0.113 0.39 0.0946 9.5 19 0.148 0.228 0.957 0.098 0.0957 0.0524 0.109 0.0182 0.057 0.0866 0.114 0.0296 0.0342 9.39 0.043 0.0872 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2023 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2023S002 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S001 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S002 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/20/13 9:55 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:00 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:10 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Analysis  Method 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8015B 8015B 8015B 8015B 8015B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Page 86 of 108 CAS Number 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 Result  Value 3.55 38.5 10.3 53.4 440 3340 199 73 102 8.19 0.112 8.18 0.124 22 13.3 0.383 32.2 0.211 0.111 0.41 310 310 900 310 2600 14600 89.1 0.454 4.85 15.1 7.52 16.8 217 2520 199 51 126 1.71 0.339 44.2 0.616 9.84 7.46 0.387 12.3 0.122 0.0552 0.206 25 25 25 25 25 25 2.4 2.4 2.4 2.4 2.4 0.62 4.3 5.3 9.7 2.1 3.1 6.5 2.4 11 2.4 2.2 1.1 4.8 11 6.6 6.6 6.6 6.6 13 240 240 240 240 240 240 22 22 22 22 22 22 22 22 22 22 22 7 22 10 22 22 22 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 6.51 38.5 10.3 53.4 440 3340 199 73 102 8.19 0.26 8.18 0.124 22 13.3 0.383 32.2 0.211 0.111 0.41 310 310 900 310 2600 14600 89.1 0.454 4.85 15.1 7.52 16.8 217 2520 199 51 126 1.71 0.339 44.2 0.616 9.84 7.46 0.387 12.3 0.487 0.0552 0.206 0.025 0.025 0.025 0.025 0.025 0.025 0.0024 0.0024 0.0024 0.0024 0.0024 0.00062 0.0043 0.0053 0.0097 0.0021 0.0031 0.0065 0.0024 0.011 0.0024 0.0022 0.0011 0.0048 0.011 6.6 6.6 6.6 6.6 13 0.24 0.24 0.24 0.24 0.24 0.24 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.007 0.022 0.01 0.022 0.022 0.022 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N N N N N N N N N N N Y Y Y Y Y Y Y N Y N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N Y N Y N N N Project  Qual  Code Validation Note U B J Q, Q Q UJ J J J J J J Q, Q Q, Q Q, Q, B Q, Q Q, Q U U U J B F B J U J U U U U U U U U U U U J F Q J U U J J U U U U U U U U U U U U U U U U U U U U U U J U J U U U F Boeing Soil Char Level  (mg/kg) 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 1400 1400 1400 1 1400 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 1400 1400 1400 1 1400 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No Yes Yes No No No No No No No No No No No No No No Yes Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No Yes No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 2.96E‐01 6.40E‐01 3.93E‐01 8.29E‐01 6.09E‐01 4.44E‐01 2.64E‐01 6.53E‐01 6.67E‐01 7.70E‐01 5.20E‐01 3.38E‐01 2.85E‐01 5.24E‐01 3.92E‐01 2.33E‐01 5.02E‐01 2.11E‐01 1.12E‐01 5.39E‐01 2.21E‐01 2.21E‐01 6.43E‐01 3.10E+02 1.86E+00 3.85E‐01 4.37E‐01 9.46E‐02 2.20E‐01 2.51E‐01 2.87E‐01 2.61E‐01 3.00E‐01 3.35E‐01 2.64E‐01 4.56E‐01 8.24E‐01 1.61E‐01 6.78E‐01 1.83E+00 1.42E+00 2.34E‐01 2.20E‐01 2.36E‐01 1.92E‐01 4.87E‐01 5.58E‐02 2.71E‐01 7.81E‐02 2.78E‐04 1.09E‐02 5.56E‐03 2.27E‐01 1.92E‐03 7.38E‐02 3.29E‐04 4.53E‐05 2.18E‐03 7.27E‐03 2.82E‐04 1.11E‐02 1.37E‐01 2.51E‐02 2.84E‐04 8.01E‐03 5.42E‐03 2.12E‐02 2.04E‐04 2.70E‐03 5.68E‐03 7.53E‐05 3.69E‐03 9.17E‐03 4.71E‐03 4.71E‐03 4.71E‐03 6.60E+00 9.29E‐03 7.50E‐01 2.67E‐03 1.04E‐01 5.33E‐02 2.18E+00 1.85E‐02 6.77E‐01 3.02E‐03 4.15E‐04 2.00E‐02 6.67E‐02 1.00E‐02 5.68E‐02 5.68E‐01 5.68E‐02 2.97E‐03 5.68E‐02 5.83E‐03 1.95E‐01 1.85E‐04 2.47E‐02 5.68E‐02 1.51E‐03 SCL Basis Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 6.51 0.977 0.651 2.6 0.651 65.1 65.1 0.651 2.6 6.51 0.26 0.521 0.13 0.26 0.26 0.13 0.521 0.521 0.13 0.13 310 310 310 310 630 12.2 0.609 0.305 6.09 0.914 0.609 2.4 0.609 60.9 60.9 0.609 2.44 6.09 0.244 0.487 0.122 0.244 0.244 0.122 0.487 0.487 0.122 0.122 25 25 25 25 25 25 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 2.4 6.6 6.6 6.6 6.6 13 240 240 240 240 240 240 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1.09 0.208 0.129 0.44 0.108 10.9 21.7 0.169 0.26 1.09 0.112 0.109 0.0599 0.125 0.0208 0.0651 0.099 0.13 0.0339 0.0391 130 130 130 130 250 9.39 0.0402 0.0816 1.01 0.107 0.11 0.67 0.101 16.4 20.3 0.134 0.244 1.01 0.0828 0.102 0.056 0.178 0.0178 0.0633 0.188 0.122 0.0244 0.0365 8.5 8.5 8.5 8.5 8.5 8.5 0.94 0.94 0.94 0.94 0.47 0.47 0.94 0.94 0.94 0.94 0.94 0.47 0.94 0.94 0.94 0.94 0.94 0.94 0.94 2.6 2.6 2.6 2.6 5.3 79 79 79 79 79 79 8.8 8.8 8.8 8.8 4.4 4.4 8.8 8.8 8.8 8.8 8.8 4.4 8.8 8.8 8.8 8.8 8.8 MDL  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2024 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2024S003 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S001 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S002 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 10:20 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:30 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 12:40 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Analytical Class PAH PAH Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Other SVOCs Analysis  Method 8270C SIM 8270C SIM 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6850 1613B 1613B 1613B 8270C SIM Analyte Phenanthrene Pyrene Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Perchlorate DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal bis(2‐Ethylhexyl) phthalate Page 87 of 108 CAS Number 85018 129000 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 14797730 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 117817 Result  Value Result  Value  Units 22 ug/kg 10 ug/kg 22600 mg/kg 123 mg/kg 0.91 mg/kg 5.01 mg/kg 30.5 mg/kg 18.5 mg/kg 35.9 mg/kg 744 mg/kg 1340 mg/kg 221 mg/kg 52.7 mg/kg 53.4 mg/kg 1.87 mg/kg 0.1 mg/kg 7.67 mg/kg 0.142 mg/kg 13.4 mg/kg 13.1 mg/kg 0.158 mg/kg 32 mg/kg 0.129 mg/kg 0.143 mg/kg 0.285 mg/kg 0.579 ng/kg 0.144 ng/kg 0.266 ng/kg 1.19 ng/kg 8.15 ng/kg 0.116 ng/kg 0.208 ng/kg 0.092 ng/kg 0.174 ng/kg 0.347 ng/kg 0.125 ng/kg 0.33 ng/kg 1.15 ng/kg 0.0658 ng/kg 0.147 ng/kg 0.185 ng/kg 0.398 ng/kg 0.0326 ng/kg 3.5 ng/kg 18.2 ng/kg 2.23 ng/kg 3.02 ng/kg 3.85 ng/kg 102 ng/kg 4.04 ng/kg 2.27 ng/kg 5.7 ng/kg 0.276 ng/kg 380 ug/kg 380 ug/kg 750 ug/kg 380 ug/kg 750 ug/kg 380 ug/kg 380 ug/kg 380 ug/kg 380 ug/kg 380 ug/kg 380 ug/kg 500 ug/kg 380 ug/kg 2500 ug/kg 2500 ug/kg 380 ug/kg 380 ug/kg 380 ug/kg 27 ug/kg 27 ug/kg 27 ug/kg 27 ug/kg 27 ug/kg 27 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 2.5 ug/kg 1.2 ug/kg 2.5 ug/kg 2.5 ug/kg 6 ug/kg 0.000145 ng/kg 0.000145 ng/kg 0.000435 ng/kg 21 ug/kg Result  in SL Units SL Units 0.022 mg/kg 0.01 mg/kg 22600 mg/kg 123 mg/kg 0.91 mg/kg 5.01 mg/kg 30.5 mg/kg 18.5 mg/kg 35.9 mg/kg 744 mg/kg 1340 mg/kg 221 mg/kg 52.7 mg/kg 53.4 mg/kg 1.87 mg/kg 0.257 mg/kg 7.67 mg/kg 0.142 mg/kg 13.4 mg/kg 13.1 mg/kg 0.129 mg/kg 32 mg/kg 0.514 mg/kg 0.143 mg/kg 0.285 mg/kg 0.000000579 mg/kg 0.000000144 mg/kg 0.000000266 mg/kg 0.00000119 mg/kg 0.00000815 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.000000174 mg/kg 0.000000347 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.00000115 mg/kg 0.00000604 mg/kg 0.000000147 mg/kg 0.00000604 mg/kg 0.000000398 mg/kg 0.00000121 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.00000385 mg/kg 0.000102 mg/kg 0.00000604 mg/kg 0.00000604 mg/kg 0.00000121 mg/kg 0.00000121 mg/kg 0.38 mg/kg 0.38 mg/kg 0.75 mg/kg 0.38 mg/kg 0.75 mg/kg 0.38 mg/kg 0.38 mg/kg 0.38 mg/kg 0.38 mg/kg 0.38 mg/kg 0.38 mg/kg 0.5 mg/kg 0.38 mg/kg 2.5 mg/kg 2.5 mg/kg 0.38 mg/kg 0.38 mg/kg 0.38 mg/kg 0.027 mg/kg 0.027 mg/kg 0.027 mg/kg 0.027 mg/kg 0.027 mg/kg 0.027 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.0012 mg/kg 0.0025 mg/kg 0.0025 mg/kg 0.006 mg/kg 1.45E‐10 mg/kg 1.45E‐10 mg/kg 4.35E‐10 mg/kg 0.021 mg/kg Detected N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y N Y N Y Y Y Y Y Y Y N N N Y Y N N Y N Y N Y N N N N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N Y Y Y N Project  Qual  Code Validation Note U J J B F B J U B U B U J UJ U U J J U UJ J U J U J UJ UJ UJ UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U F, B B M, B, F F, B B B F, B M, F, B F, B F, B F, B B, F M M, F, B M, F, B M, F, B M, F, B F, B F, B M, F, B M, F, B M, F, B M, F, B F B F Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 1.3 No 1.69E‐02 Ecological RBSL 1.2 No 8.33E‐03 Ecological RBSL 37900 No 5.96E‐01 Background 203.8 No 6.04E‐01 Background 4.8 No 1.90E‐01 Ecological RBSL 22 No 2.28E‐01 Ecological RBSL 60.11 No 5.07E‐01 Background 26.18 No 7.07E‐01 Background 64.4 No 5.57E‐01 Background 723 Yes 1.03E+00 Background 7524 No 1.78E‐01 Background 754 No 2.93E‐01 Background 111.8 No 4.71E‐01 Background 153 No 3.49E‐01 Background 10.64 No 1.76E‐01 Background 0.5 No 5.14E‐01 MRL 24.2 No 3.17E‐01 Background 0.435 No 3.26E‐01 Background 42 No 3.19E‐01 Background 33.9 No 3.86E‐01 Background 1.642 No 7.86E‐02 Background 64.2 No 4.98E‐01 Background 1 No 5.14E‐01 MRL 0.99 No 1.44E‐01 Ecological RBSL 0.761 No 3.75E‐01 Suburban Residential RBSL 0.0000057 No 1.02E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 4.72E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 4.13E‐01 Ecological RBSL 0.3 Yes 1.27E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.27E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 4.55E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL 0.3 Yes 1.27E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.32 No 8.44E‐02 Ecological RBSL 90 No 3.00E‐04 Ecological RBSL 2.3 No 1.17E‐02 Ecological RBSL 4.5 No 6.00E‐03 Ecological RBSL 0.11 No 2.45E‐01 Ecological RBSL 13 No 2.08E‐03 Ecological RBSL 0.0325 No 7.69E‐02 Suburban Residential RBSL 7.29 No 3.43E‐04 Suburban Residential RBSL 53 No 4.72E‐05 Ecological RBSL 1.1 No 2.27E‐03 Ecological RBSL 0.33 No 7.58E‐03 Ecological RBSL 2.2 No 1.14E‐03 Ecological RBSL 0.387 No 6.46E‐03 Suburban Residential RBSL 0.0387 No 6.46E‐02 Suburban Residential RBSL 0.387 No 6.46E‐03 Suburban Residential RBSL 7.4 No 3.38E‐04 Ecological RBSL 0.387 No 6.46E‐03 Suburban Residential RBSL 1.2 No 2.08E‐03 Ecological RBSL 0.113 No 2.21E‐02 Suburban Residential RBSL 54 No 4.63E‐05 Ecological RBSL 0.89 No 2.81E‐03 Ecological RBSL 0.387 No 6.46E‐03 Suburban Residential RBSL 14.6 No 8.22E‐05 Suburban Residential RBSL 1.3 No 1.92E‐03 Ecological RBSL 1.2 No 2.08E‐03 Ecological RBSL 0.5 No 1.20E‐02 Ecological RBSL 0.0000057 No 2.54E‐05 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 7.73E‐04 Background 0.32 No 6.56E‐02 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 22 22 12.9 0.643 0.321 6.43 0.964 0.643 2.6 0.643 64.3 64.3 0.643 2.57 6.43 0.257 0.514 0.129 0.257 0.257 0.129 0.514 0.514 0.129 0.129 ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 8.8 8.8 9.91 0.0424 0.0862 1.07 0.113 0.116 0.71 0.107 17.4 21.5 0.141 0.257 1.07 0.0874 0.108 0.0592 0.188 0.0188 0.0669 0.198 0.129 0.0257 0.0386 ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 6.04 6.04 6.04 6.04 6.04 6.04 6.04 6.04 6.04 6.04 6.04 6.04 6.04 1.21 1.21 6.04 6.04 6.04 6.04 12.1 12.1 6.04 6.04 1.21 1.21 380 380 750 380 750 380 380 380 380 380 380 500 380 2500 2500 380 380 380 27 27 27 27 27 27 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 6 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0139 0.0319 0.0167 0.0266 0.0358 0.0263 0.0375 0.0272 0.0348 0.0448 0.0402 0.0261 0.0395 0.0566 0.0319 0.0152 0.0319 0.0265 0.036 0.0221 0.0315 0.042 0.0402 0.0566 0.0319 130 130 250 130 250 130 130 250 310 190 250 310 130 1900 1900 160 130 190 8.9 8.9 8.9 8.9 8.9 8.9 0.99 0.99 0.99 0.99 0.5 0.5 0.99 0.99 0.99 0.99 0.99 0.5 0.99 0.99 0.99 0.99 0.99 0.99 0.99 3.1 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 21 ug/kg 7.1 ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2025 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2025S003 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S001 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/14/13 13:00 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:50 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 6850 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl Perchlorate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Page 88 of 108 CAS Number 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 14797730 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 Result  Value 21 21 21 21 21 2 2 0.83 2 2 0.47 2 2 0.86 2 2 0.82 2 1.7 2 2 0.98 1.7 1.7 0.0942 0.229 0.105 0.053 0.0257 0.0261 0.0272 0.0429 0.049 0.0517 0.0364 0.0509 0.0478 0.0283 0.035 0.55 0.407 0.431 0.502 0.171 1.45 0.215 0.335 0.108 0.227 360 360 720 360 720 360 360 360 360 360 360 480 360 2400 2400 360 360 360 4.8 21100 110 0.807 4.39 24.5 6.29 24.4 330 2430 88.4 44.5 50.8 4.35 0.159 8.85 0.14 12.1 10 0.622 15.8 0.152 0.0705 0.271 23 23 23 23 23 23 2.1 2.1 2.1 2.1 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00083 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00047 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00086 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00082 mg/kg 0.002 mg/kg 0.0017 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00098 mg/kg 0.0017 mg/kg 0.0017 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000118 mg/kg 0.00000118 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.0000118 mg/kg 0.00000145 mg/kg 0.00000589 mg/kg 0.00000589 mg/kg 0.00000118 mg/kg 0.00000118 mg/kg 0.36 mg/kg 0.36 mg/kg 0.72 mg/kg 0.36 mg/kg 0.72 mg/kg 0.36 mg/kg 0.36 mg/kg 0.36 mg/kg 0.36 mg/kg 0.36 mg/kg 0.36 mg/kg 0.48 mg/kg 0.36 mg/kg 2.4 mg/kg 2.4 mg/kg 0.36 mg/kg 0.36 mg/kg 0.36 mg/kg 0.0048 mg/kg 21100 mg/kg 110 mg/kg 0.807 mg/kg 4.39 mg/kg 24.5 mg/kg 6.29 mg/kg 24.4 mg/kg 330 mg/kg 2430 mg/kg 88.4 mg/kg 44.5 mg/kg 50.8 mg/kg 4.35 mg/kg 0.231 mg/kg 8.85 mg/kg 0.14 mg/kg 12.1 mg/kg 10 mg/kg 0.622 mg/kg 15.8 mg/kg 0.152 mg/kg 0.0705 mg/kg 0.271 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.023 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg 0.0021 mg/kg Detected N N N N N N N Y N N Y N N Y N N Y N Y N N Y Y Y N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N N N N N N N N N Project  Qual  Code U U U U U U U J U U J U U J U U J U J U U J J J U UJ U UJ U U U UJ U UJ U UJ UJ U U UJ UJ UJ UJ UJ J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U Validation Note F, B M, B B, F M, F, B B B M, F, B F, B M, F, B F, B M, F, B M, F, B M, F, B M, F, B B, M, F M, F, B M, F, B F, B M, F, B M, F, B M, F, B M, F, B B Q, Q J J Q Q F J U Q, Q, B F J J U U U U U U U U U U F, F F F, F Q, Q, F Boeing Soil Char Level  (mg/kg) 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 0.5 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 2.33E‐04 9.13E‐03 4.67E‐03 1.91E‐01 1.62E‐03 6.15E‐02 2.74E‐04 1.57E‐05 1.82E‐03 6.06E‐03 2.14E‐04 5.17E‐03 5.17E‐02 2.22E‐03 2.70E‐04 5.17E‐03 6.83E‐04 1.77E‐02 3.15E‐05 2.25E‐03 5.17E‐03 6.71E‐05 1.31E‐03 1.42E‐03 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.91E‐01 1.20E+00 No SL No SL No SL No SL 1.20E+00 No SL No SL No SL No SL 4.36E‐03 No SL No SL No SL 1.20E+00 No SL No SL 9.60E‐03 5.57E‐01 5.40E‐01 1.68E‐01 2.00E‐01 4.08E‐01 2.40E‐01 3.79E‐01 4.56E‐01 3.23E‐01 1.17E‐01 3.98E‐01 3.32E‐01 4.09E‐01 4.62E‐01 3.66E‐01 3.22E‐01 2.88E‐01 2.95E‐01 3.79E‐01 2.46E‐01 1.52E‐01 7.12E‐02 3.56E‐01 7.19E‐02 2.56E‐04 1.00E‐02 5.11E‐03 2.09E‐01 1.77E‐03 6.46E‐02 2.88E‐04 3.96E‐05 1.91E‐03 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 21 21 21 21 21 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 5.89 5.89 5.89 5.89 5.89 5.89 5.89 5.89 5.89 5.89 5.89 5.89 5.89 1.18 1.18 5.89 5.89 5.89 5.89 11.8 11.8 5.89 5.89 1.18 1.18 360 360 720 360 720 360 360 360 360 360 360 480 360 2400 2400 360 360 360 4.8 11.6 0.578 0.289 5.78 0.867 0.578 2.3 0.578 57.8 57.8 0.578 2.31 5.78 0.231 0.462 0.116 0.231 0.231 0.116 0.462 0.462 0.116 0.116 23 23 23 23 23 23 2.1 2.1 2.1 2.1 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 7.1 7.1 7.1 7.1 7.1 0.79 0.79 0.79 0.79 0.39 0.39 0.79 0.79 0.79 0.79 0.79 0.39 0.79 0.79 0.79 0.79 0.79 0.79 0.79 0.0205 0.0319 0.0281 0.0171 0.0257 0.016 0.0272 0.017 0.0269 0.0214 0.0364 0.0147 0.0193 0.0283 0.035 0.0237 0.0319 0.0161 0.0266 0.0331 0.0342 0.0203 0.0364 0.0283 0.035 120 120 240 120 240 120 120 240 300 180 240 300 120 1800 1800 150 120 180 2.5 8.91 0.0381 0.0774 0.959 0.102 0.104 0.64 0.0959 15.6 19.3 0.127 0.231 0.959 0.0786 0.0971 0.0532 0.169 0.0169 0.0601 0.178 0.116 0.0231 0.0347 7.7 7.7 7.7 7.7 7.7 7.7 0.85 0.85 0.85 0.85 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2026 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S002 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2026S003 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S001 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 9:55 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 10:00 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:25 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 Analyte Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Page 89 of 108 CAS Number 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 Result  Value 2.1 2.1 2.1 2.1 2.8 2.1 2.1 2.4 2.1 3.1 2.1 2.1 0.99 1.4 3.2 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 15000 111 0.496 3.09 21 5.37 35 252 2290 184 32.4 52.4 3.46 0.0745 19.8 0.123 9.02 3.45 0.361 16.5 0.11 0.0219 0.233 16000 97.4 0.664 3.92 20 6.15 15.6 347 2680 86.8 36.4 40.4 3.09 0.124 6.17 0.177 16.8 7.44 0.708 13.6 0.157 0.0374 0.294 20800 49.1 0.904 3.48 28.7 5.81 38.1 312 1790 1170 45.7 51.2 4.42 0.19 25.8 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 0.0021 0.0021 0.0021 0.0021 0.0028 0.0021 0.0021 0.0024 0.0021 0.0031 0.0021 0.0021 0.00099 0.0014 0.0032 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 15000 111 0.496 3.09 21 5.37 35 252 2290 184 32.4 52.4 3.46 0.219 19.8 0.123 9.02 3.45 0.11 16.5 0.438 0.11 0.233 16000 97.4 0.664 3.92 20 6.15 15.6 347 2680 86.8 36.4 40.4 3.09 0.236 6.17 0.177 16.8 7.44 0.708 13.6 0.157 0.0374 0.294 20800 49.1 0.904 3.48 28.7 5.81 38.1 312 1790 1170 45.7 51.2 4.42 0.251 25.8 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected N N N N Y N N Y N Y N N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y N Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Project  Qual  Code Validation Note U U U U UJ U Q, Q UJ Q, Q U UJ J J U U U U U U U U U U U U U U U U U U U U U U U U U Q, Q F, F F F, F F Q, Q J J Q Q F J UJ Q, Q U F U U Q, Q J J Q Q F J U Q, Q, B F J J Q, Q J J Q Q F J U Q, Q, B Boeing Soil Char Level  (mg/kg) 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No Yes Ratio Boeing Soil Char Level 6.36E‐03 9.55E‐04 5.43E‐03 5.43E‐02 7.24E‐03 2.84E‐04 5.43E‐03 2.00E‐03 1.86E‐02 5.74E‐05 2.36E‐03 5.43E‐03 6.78E‐05 1.08E‐03 2.67E‐03 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 1.50E‐03 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 3.96E‐01 5.45E‐01 1.03E‐01 1.40E‐01 3.49E‐01 2.05E‐01 5.43E‐01 3.49E‐01 3.04E‐01 2.44E‐01 2.90E‐01 3.42E‐01 3.25E‐01 4.38E‐01 8.18E‐01 2.83E‐01 2.15E‐01 1.02E‐01 6.70E‐02 2.57E‐01 4.38E‐01 1.11E‐01 3.06E‐01 4.22E‐01 4.78E‐01 1.38E‐01 1.78E‐01 3.33E‐01 2.35E‐01 2.42E‐01 4.80E‐01 3.56E‐01 1.15E‐01 3.26E‐01 2.64E‐01 2.90E‐01 4.72E‐01 2.55E‐01 4.07E‐01 4.00E‐01 2.19E‐01 4.31E‐01 2.12E‐01 1.57E‐01 3.78E‐02 3.86E‐01 5.49E‐01 2.41E‐01 1.88E‐01 1.58E‐01 4.77E‐01 2.22E‐01 5.92E‐01 4.32E‐01 2.38E‐01 1.55E+00 4.09E‐01 3.35E‐01 4.15E‐01 5.02E‐01 1.07E+00 SCL Basis Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 2.1 20 20 20 20 20 20 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 11 0.548 0.274 5.48 0.822 0.548 2.2 0.548 54.8 54.8 0.548 2.19 5.48 0.219 0.438 0.11 0.219 0.219 0.11 0.438 0.438 0.11 0.11 11.8 0.591 0.295 5.91 0.886 0.591 2.4 0.591 59.1 59.1 0.591 2.36 5.91 0.236 0.472 0.118 0.236 0.236 0.118 0.472 0.472 0.118 0.118 12.5 0.627 0.313 6.27 0.94 0.627 2.5 0.627 62.7 62.7 0.627 2.51 6.27 0.251 0.501 RL Units MDL ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.43 0.43 0.85 0.85 0.85 0.85 0.85 0.43 0.85 0.85 0.85 0.85 0.85 0.85 0.85 6.6 6.6 6.6 6.6 6.6 6.6 0.74 0.74 0.74 0.74 0.37 0.37 0.74 0.74 0.74 0.74 0.74 0.37 0.74 0.74 0.74 0.74 0.74 0.74 0.74 8.45 0.0361 0.0734 0.909 0.0964 0.0986 0.6 0.0909 14.8 18.3 0.12 0.219 0.909 0.0745 0.092 0.0504 0.16 0.016 0.057 0.169 0.11 0.0219 0.0329 9.11 0.039 0.0791 0.98 0.104 0.106 0.65 0.098 15.9 19.7 0.13 0.236 0.98 0.0803 0.0992 0.0543 0.172 0.0172 0.0614 0.182 0.118 0.0236 0.0354 9.67 0.0414 0.084 1.04 0.11 0.113 0.69 0.104 16.9 20.9 0.138 0.251 1.04 0.0853 0.105 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2028 ELBS2034 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S002 ELBS2028S003 ELBS2028S003 ELBS2034S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S001 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 11:30 6/11/13 12:00 6/11/13 12:00 6/20/13 11:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:30 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 8.5 8.5 14.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 9 9 15.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Analysis  Method 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A Analyte Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Sodium Arsenic Selenium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene Page 90 of 108 CAS Number 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7440235 7440382 7782492 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 Result  Value 0.0883 11.1 5.98 0.211 22.1 0.125 0.056 0.26 459 42.7 0.109 24900 141 0.85 6.73 26.9 9.7 23.6 376 3290 141 50 48.1 5.48 0.102 5.09 0.199 12.5 7.24 0.477 18.3 0.144 0.0402 0.323 0 0 0 6.1 6.1 12 6.1 46 22 22 22 22 22 22 2 2 2 2 2 2 2 2 2 2 2 0.52 2 2 2 2 2 2 2 0.0305 0.158 0.0196 0.0174 0.0313 0.016 0.0513 0.0619 0.0935 0.089 0.0417 0.0191 0.0387 0.0323 0.035 0.0979 0.355 0.282 0.636 0.113 0.771 0.49 0.233 0.135 0.159 330 330 670 330 670 330 330 330 330 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.0883 mg/kg 11.1 mg/kg 5.98 mg/kg 0.125 mg/kg 22.1 mg/kg 0.501 mg/kg 0.056 mg/kg 0.26 mg/kg 459 mg/kg 42.7 mg/kg 0.436 mg/kg 24900 mg/kg 141 mg/kg 0.85 mg/kg 6.73 mg/kg 26.9 mg/kg 9.7 mg/kg 23.6 mg/kg 376 mg/kg 3290 mg/kg 141 mg/kg 50 mg/kg 48.1 mg/kg 5.48 mg/kg 0.237 mg/kg 5.09 mg/kg 0.199 mg/kg 12.5 mg/kg 7.24 mg/kg 0.477 mg/kg 18.3 mg/kg 0.144 mg/kg 0.0402 mg/kg 0.323 mg/kg 0 mg/kg 0 mg/kg 0 mg/kg 6.1 mg/kg 6.1 mg/kg 12 mg/kg 6.1 mg/kg 46 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00052 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.00000122 mg/kg 0.00000122 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.0000122 mg/kg 0.0000122 mg/kg 0.0000061 mg/kg 0.0000061 mg/kg 0.00000122 mg/kg 0.00000122 mg/kg 0.33 mg/kg 0.33 mg/kg 0.67 mg/kg 0.33 mg/kg 0.67 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg Detected Y Y Y N Y N Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N N N N N Y N Y N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note J U F U J U F F J U B B J J U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U UJ UJ U UJ UJ UJ UJ UJ U UJ U UJ UJ U U UJ UJ UJ UJ UJ U UJ UJ UJ UJ U U U U U U U U U F F L M, F M, F, B F, B M, F, B M, F M, F, B M M F, B M, F, B F M, F M, F, B B F M, F, B M, F, B M, F, B M, F, B M, F, B F, B M, F, B M, F, B M, B M, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.435 No 2.03E‐01 Background 42 No 2.64E‐01 Background 33.9 No 1.76E‐01 Background 1.642 No 7.61E‐02 Background 64.2 No 3.44E‐01 Background 1 No 5.01E‐01 MRL 0.99 No 5.66E‐02 Ecological RBSL 0.761 No 3.42E‐01 Suburban Residential RBSL 754 No 6.09E‐01 Background 24.2 Yes 1.76E+00 Background 1 No 4.36E‐01 MRL 37900 No 6.57E‐01 Background 203.8 No 6.92E‐01 Background 4.8 No 1.77E‐01 Ecological RBSL 22 No 3.06E‐01 Ecological RBSL 60.11 No 4.48E‐01 Background 26.18 No 3.71E‐01 Background 64.4 No 3.66E‐01 Background 723 No 5.20E‐01 Background 7524 No 4.37E‐01 Background 754 No 1.87E‐01 Background 111.8 No 4.47E‐01 Background 153 No 3.14E‐01 Background 10.64 No 5.15E‐01 Background 0.5 No 4.74E‐01 MRL 24.2 No 2.10E‐01 Background 0.435 No 4.57E‐01 Background 42 No 2.98E‐01 Background 33.9 No 2.14E‐01 Background 1.642 No 2.90E‐01 Background 64.2 No 2.85E‐01 Background 1 No 1.44E‐01 MRL 0.99 No 4.06E‐02 Ecological RBSL 0.761 No 4.24E‐01 Suburban Residential RBSL 0.0000057 No 0.00E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 0.00E+00 Background 1400 No 4.36E‐03 1400 No 4.36E‐03 1400 No 8.57E‐03 1 Yes 6.10E+00 1400 No 3.29E‐02 0.32 No 6.88E‐02 Ecological RBSL 90 No 2.44E‐04 Ecological RBSL 2.3 No 9.57E‐03 Ecological RBSL 4.5 No 4.89E‐03 Ecological RBSL 0.11 No 2.00E‐01 Ecological RBSL 13 No 1.69E‐03 Ecological RBSL 0.0325 No 6.15E‐02 Suburban Residential RBSL 7.29 No 2.74E‐04 Suburban Residential RBSL 53 No 3.77E‐05 Ecological RBSL 1.1 No 1.82E‐03 Ecological RBSL 0.33 No 6.06E‐03 Ecological RBSL 2.2 No 9.09E‐04 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 0.0387 No 5.17E‐02 Suburban Residential RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 7.4 No 2.70E‐04 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 1.2 No 4.33E‐04 Ecological RBSL 0.113 No 1.77E‐02 Suburban Residential RBSL 54 No 3.70E‐05 Ecological RBSL 0.89 No 2.25E‐03 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 14.6 No 1.37E‐04 Suburban Residential RBSL 1.3 No 1.54E‐03 Ecological RBSL 1.2 No 1.67E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 3.59E‐01 Ecological RBSL 0.3 Yes 1.10E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.10E+00 MRL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 0.125 0.251 0.251 0.125 0.501 0.501 0.125 0.125 64 0.512 0.436 11.8 0.591 0.296 5.91 0.887 0.591 2.4 0.591 59.1 59.1 0.591 2.37 5.91 0.237 0.473 0.118 0.237 0.237 0.118 0.473 0.473 0.118 0.118 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.0577 0.183 0.0183 0.0652 0.193 0.125 0.0251 0.0376 21.4 0.108 0.109 8.53 0.039 0.0792 0.993 0.189 0.117 0.4 0.0982 9.86 19.7 0.154 0.237 0.993 0.102 0.0993 0.0544 0.114 0.0189 0.0591 0.0899 0.118 0.0307 0.0355 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 6.1 6.1 6.1 6.1 12 22 22 22 22 22 22 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 6.1 6.1 6.1 6.1 6.1 6.1 6.1 6.1 6.1 6.1 6.1 6.1 6.1 1.22 1.22 6.1 6.1 6.1 6.1 12.2 12.2 6.1 6.1 1.22 1.22 330 330 670 330 670 330 330 330 330 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 2.4 2.4 2.4 2.4 4.9 7.2 7.2 7.2 7.2 7.2 7.2 0.8 0.8 0.8 0.8 0.4 0.4 0.8 0.8 0.8 0.8 0.8 0.4 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.013 0.0399 0.0196 0.0166 0.0262 0.0158 0.0286 0.02 0.0274 0.0234 0.0417 0.0152 0.0235 0.0323 0.035 0.0163 0.0399 0.0168 0.0274 0.0357 0.0344 0.0235 0.0417 0.0323 0.035 110 110 220 110 220 110 110 220 280 mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S002 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:40 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 Sample  Bottom  Depth (feet bgs) 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 1613B 1613B 1613B 1613B 8015B 8015B 8015B 8015B 8015B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) C30‐C40 (Heavy Oil Range) bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Page 91 of 108 CAS Number 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 24959679 16887006 16984488 NO3 NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 ORO C30‐C40 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 Result  Value 330 330 450 330 2200 2200 330 330 330 0.12 2.4 3.3 46 0.49 0.12 16.1 28500 147 1.19 7.71 37.8 8.02 44.4 316 3510 327 63.1 69.5 7.22 0.105 11.5 0.145 17.1 8.23 0.289 26.4 0.122 0.0841 0.419 21 21 21 21 21 21 21 21 21 0.000577 0.000577 0.00173 0.0298 6.1 6.1 6.1 6.1 12 22 22 22 22 22 22 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 0.068 0.661 0.0479 0.0369 0.0229 0.0193 0.0607 0.0769 0.0987 0.0558 0.0482 0.0225 0.0166 0.0265 0.329 1.32 0.488 0.732 0.136 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.33 mg/kg 0.33 mg/kg 0.45 mg/kg 0.33 mg/kg 2.2 mg/kg 2.2 mg/kg 0.33 mg/kg 0.33 mg/kg 0.33 mg/kg 2.4 mg/kg 2.4 mg/kg 3.3 mg/kg 46 mg/kg 1.2 mg/kg 6.1 mg/kg 16.1 mg/kg 28500 mg/kg 147 mg/kg 1.19 mg/kg 7.71 mg/kg 37.8 mg/kg 8.02 mg/kg 44.4 mg/kg 316 mg/kg 3510 mg/kg 327 mg/kg 63.1 mg/kg 69.5 mg/kg 7.22 mg/kg 0.245 mg/kg 11.5 mg/kg 0.145 mg/kg 17.1 mg/kg 8.23 mg/kg 0.289 mg/kg 26.4 mg/kg 0.49 mg/kg 0.0841 mg/kg 0.419 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 5.77E‐10 mg/kg 5.77E‐10 mg/kg 1.73E‐09 mg/kg 0.00000121 mg/kg 6.1 mg/kg 6.1 mg/kg 6.1 mg/kg 6.1 mg/kg 12 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000121 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.0000121 mg/kg Detected N N N N N N N N N N Y Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y N N N N N N N N N Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note U U U U U U U U U U J U U F F F U B B U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ UJ U UJ U U U UJ UJ UJ UJ UJ U UJ UJ UJ UJ UJ U F F L M, F, B M, F, B F, B M, F, B F, B F, B B M, B M, F, B M, F, B M, F, B M, F, B F, B M, F, B M, F M, F M, F M, F, B F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL 110 No 4.09E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.3 Yes 1.10E+00 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 9.43E‐02 Ecological RBSL 2340 No 1.97E‐02 Ecological RBSL ‐‐ No SL No SL 863.2 No 7.07E‐03 Background ‐‐ No SL No SL 37900 No 7.52E‐01 Background 203.8 No 7.21E‐01 Background 4.8 No 2.48E‐01 Ecological RBSL 22 No 3.50E‐01 Ecological RBSL 60.11 No 6.29E‐01 Background 26.18 No 3.06E‐01 Background 64.4 No 6.89E‐01 Background 723 No 4.37E‐01 Background 7524 No 4.67E‐01 Background 754 No 4.34E‐01 Background 111.8 No 5.64E‐01 Background 153 No 4.54E‐01 Background 10.64 No 6.79E‐01 Background 0.5 No 4.90E‐01 MRL 24.2 No 4.75E‐01 Background 0.435 No 3.33E‐01 Background 42 No 4.07E‐01 Background 33.9 No 2.43E‐01 Background 1.642 No 1.76E‐01 Background 64.2 No 4.11E‐01 Background 1 No 4.90E‐01 MRL 0.99 No 8.49E‐02 Ecological RBSL 0.761 No 5.51E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.75E‐01 Ecological RBSL 0.18 No 1.17E‐01 Ecological RBSL 0.082 No 2.56E‐01 Ecological RBSL 0.043 No 4.88E‐01 Ecological RBSL 0.017 Yes 1.24E+00 MRL 0.039 No 5.38E‐01 Ecological RBSL 0.025 No 8.40E‐01 Ecological RBSL 0.0000057 No 1.01E‐04 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 3.07E‐03 Background ‐‐ No SL No SL 1400 No 4.36E‐03 1400 No 4.36E‐03 1400 No 4.36E‐03 1 Yes 6.10E+00 1400 No 8.57E‐03 0.32 No 6.88E‐02 Ecological RBSL 90 No 2.44E‐04 Ecological RBSL 2.3 No 9.57E‐03 Ecological RBSL 4.5 No 4.89E‐03 Ecological RBSL 0.11 No 2.00E‐01 Ecological RBSL 13 No 1.69E‐03 Ecological RBSL 0.0325 No 6.15E‐02 Suburban Residential RBSL 7.29 No 2.74E‐04 Suburban Residential RBSL 53 No 3.77E‐05 Ecological RBSL 1.1 No 1.82E‐03 Ecological RBSL 0.33 No 6.06E‐03 Ecological RBSL 2.2 No 9.09E‐04 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 0.0387 No 5.17E‐02 Suburban Residential RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 7.4 No 2.70E‐04 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 1.2 No 1.67E‐03 Ecological RBSL 0.113 No 1.77E‐02 Suburban Residential RBSL 54 No 3.70E‐05 Ecological RBSL 0.89 No 2.25E‐03 Ecological RBSL 0.387 No 5.17E‐03 Suburban Residential RBSL 14.6 No 1.37E‐04 Suburban Residential RBSL 1.3 No 1.54E‐03 Ecological RBSL 1.2 No 1.67E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 330 330 450 330 2200 2200 330 330 330 2.4 6.1 1.2 5.3 1.2 6.1 6.1 12.2 0.612 0.306 6.12 0.918 0.612 2.4 0.612 61.2 61.2 0.612 2.45 6.12 0.245 0.49 0.122 0.245 0.245 0.122 0.49 0.49 0.122 0.122 21 21 21 21 21 21 21 21 21 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 170 220 280 110 1700 1700 140 110 170 0.12 1.2 0.49 2.2 0.49 0.12 1.9 8.82 0.0404 0.082 1.03 0.196 0.121 0.42 0.102 10.2 20.4 0.159 0.245 1.03 0.105 0.103 0.0563 0.118 0.0196 0.0612 0.093 0.122 0.0318 0.0367 4 4 4.4 5.6 9.7 4 4 4 5.9 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1.21 6.1 6.1 6.1 6.1 12 22 22 22 22 22 22 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 6.07 6.07 6.07 6.07 6.07 6.07 6.07 6.07 6.07 6.07 6.07 6.07 6.07 1.21 6.07 6.07 6.07 6.07 12.1 ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0298 2.4 2.4 2.4 2.4 4.8 7.2 7.2 7.2 7.2 7.2 7.2 0.8 0.8 0.8 0.8 0.4 0.4 0.8 0.8 0.8 0.8 0.8 0.4 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.0137 0.0277 0.0166 0.0143 0.0229 0.0134 0.0237 0.0159 0.0238 0.0174 0.0282 0.0133 0.0166 0.0263 0.015 0.0277 0.0141 0.0234 0.0244 ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2035 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2035S003 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S001 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/19/13 13:50 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:05 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Sample  Bottom  Depth (feet bgs) 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 1613B 1613B 1613B 1613B 1613B 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 8330A 300.0 300.0 300.0 300.0 300.0 300.0 300.0 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 Analyte Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl Bromide Chloride Fluoride Nitrate‐NO3 Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Page 92 of 108 CAS Number 3268879 30402154 36088229 55722275 41903575 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 24959679 16887006 16984488 NO3 NO2 14265442 14808798 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 Result  Value 5.77 0.378 0.573 0.0976 0.244 350 350 700 350 700 350 350 350 350 350 350 460 350 2300 2300 350 350 350 0.12 3 1.4 5.8 0.48 0.12 10.5 30100 114 1.1 6.35 60.1 8.59 45.9 250 6510 257 56.3 86.6 9.2 0.105 2.7 0.0561 22.6 6.57 0.136 23.7 0.191 0.145 0.541 20 20 20 20 20 20 20 20 20 17200 101 0.636 3.84 20.4 7.18 18.3 308 2790 80.1 39.5 47.6 4.15 0.101 4.41 0.179 13 10.3 0.446 13.5 0.119 0.0429 0.256 19700 104 0.735 3.78 25.2 7.22 22.3 409 3380 168 46.2 53.5 4.65 0.104 6.15 0.218 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.00000577 mg/kg 0.00000607 mg/kg 0.00000607 mg/kg 0.00000121 mg/kg 0.00000121 mg/kg 0.35 mg/kg 0.35 mg/kg 0.7 mg/kg 0.35 mg/kg 0.7 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 0.46 mg/kg 0.35 mg/kg 2.3 mg/kg 2.3 mg/kg 0.35 mg/kg 0.35 mg/kg 0.35 mg/kg 2.4 mg/kg 3 mg/kg 1.4 mg/kg 5.8 mg/kg 1.2 mg/kg 6.1 mg/kg 10.5 mg/kg 30100 mg/kg 114 mg/kg 1.1 mg/kg 6.35 mg/kg 60.1 mg/kg 8.59 mg/kg 45.9 mg/kg 250 mg/kg 6510 mg/kg 257 mg/kg 56.3 mg/kg 86.6 mg/kg 9.2 mg/kg 0.244 mg/kg 2.7 mg/kg 0.122 mg/kg 22.6 mg/kg 6.57 mg/kg 0.136 mg/kg 23.7 mg/kg 0.191 mg/kg 0.145 mg/kg 0.541 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 17200 mg/kg 101 mg/kg 0.636 mg/kg 5.88 mg/kg 20.4 mg/kg 7.18 mg/kg 18.3 mg/kg 308 mg/kg 2790 mg/kg 80.1 mg/kg 39.5 mg/kg 47.6 mg/kg 4.15 mg/kg 0.235 mg/kg 4.41 mg/kg 0.179 mg/kg 13 mg/kg 10.3 mg/kg 0.446 mg/kg 13.5 mg/kg 0.119 mg/kg 0.0429 mg/kg 0.256 mg/kg 19700 mg/kg 104 mg/kg 0.735 mg/kg 6.02 mg/kg 25.2 mg/kg 7.22 mg/kg 22.3 mg/kg 409 mg/kg 3380 mg/kg 168 mg/kg 46.2 mg/kg 53.5 mg/kg 4.65 mg/kg 0.241 mg/kg 6.15 mg/kg 0.218 mg/kg Detected Y N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N Y Y Y Y Y Y Y N N N N N N N N N Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Project  Qual  Code J UJ UJ UJ UJ U U U U U U U U U U U U U U U U U U U J Validation Note F, B M, F M, F M, B M, F U U F F F U U B B J U U U U U U U U U Q, Q U B J Q, Q Q J UJ Q, Q Q, Q J J Q, Q, B Q, Q J J J Q, Q Q, Q U B J Q, Q Q J UJ Q, Q Q, Q Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 ‐‐ ‐‐ 0.12 0.18 0.082 0.043 0.017 0.039 0.025 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 42 33.9 1.642 64.2 1 0.99 0.761 37900 203.8 4.8 22 60.11 26.18 64.4 723 7524 754 111.8 153 10.64 0.5 24.2 0.435 Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No Yes No SL No SL No SL No SL Yes No SL No SL No SL No SL No No SL No SL No SL Yes No SL No SL No SL No SL No No No SL No No SL No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL 3.80E‐01 1.17E+00 No SL No SL No SL No SL 1.17E+00 No SL No SL No SL No SL 4.18E‐03 No SL No SL No SL 1.17E+00 No SL No SL No SL No SL 4.00E‐02 2.48E‐03 No SL 7.07E‐03 No SL 7.94E‐01 5.59E‐01 2.29E‐01 2.89E‐01 1.00E+00 3.28E‐01 7.13E‐01 3.46E‐01 8.65E‐01 3.41E‐01 5.04E‐01 5.66E‐01 8.65E‐01 4.88E‐01 1.12E‐01 2.80E‐01 5.38E‐01 1.94E‐01 8.28E‐02 3.69E‐01 1.91E‐01 1.46E‐01 7.11E‐01 No SL No SL 1.67E‐01 1.11E‐01 2.44E‐01 4.65E‐01 1.18E+00 5.13E‐01 8.00E‐01 4.54E‐01 4.96E‐01 1.33E‐01 2.67E‐01 3.39E‐01 2.74E‐01 2.84E‐01 4.26E‐01 3.71E‐01 1.06E‐01 3.53E‐01 3.11E‐01 3.90E‐01 4.70E‐01 1.82E‐01 4.11E‐01 3.10E‐01 3.04E‐01 2.72E‐01 2.10E‐01 1.19E‐01 4.33E‐02 3.36E‐01 5.20E‐01 5.10E‐01 1.53E‐01 2.74E‐01 4.19E‐01 2.76E‐01 3.46E‐01 5.66E‐01 4.49E‐01 2.23E‐01 4.13E‐01 3.50E‐01 4.37E‐01 4.82E‐01 2.54E‐01 5.01E‐01 SCL Basis Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL Ecological RBSL Background Background Background Background Background Background Background Background Background MRL Background Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 12.1 6.07 6.07 1.21 1.21 350 350 700 350 700 350 350 350 350 350 350 460 350 2300 2300 350 350 350 2.4 6.1 1.2 5.3 1.2 6.1 6.1 12.2 0.61 0.305 6.1 0.915 0.61 2.4 0.61 61 61 0.61 2.44 6.1 0.244 0.488 0.122 0.244 0.244 0.122 0.488 0.488 0.122 0.122 20 20 20 20 20 20 20 20 20 11.8 0.588 0.294 5.88 0.881 0.588 2.4 0.588 58.8 58.8 0.588 2.35 5.88 0.235 0.47 0.118 0.235 0.235 0.118 0.47 0.47 0.118 0.118 12 0.602 0.301 6.02 0.903 0.602 2.4 0.602 60.2 60.2 0.602 2.41 6.02 0.241 0.482 0.12 RL Units MDL ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.0241 0.0171 0.0282 0.0235 0.0263 120 120 230 120 230 120 120 230 290 170 230 290 120 1700 1700 150 120 180 0.12 1.2 0.48 2.1 0.48 0.12 1.9 8.79 0.0402 0.0817 1.02 0.195 0.121 0.41 0.101 10.2 20.4 0.159 0.244 1.02 0.105 0.102 0.0561 0.117 0.0195 0.061 0.0927 0.122 0.0317 0.0366 4 4 4.3 5.5 9.6 4 4 4 5.9 8.47 0.0388 0.0787 0.987 0.188 0.116 0.4 0.0975 9.8 19.6 0.153 0.235 0.987 0.101 0.0987 0.0541 0.113 0.0188 0.0588 0.0893 0.118 0.0306 0.0353 8.68 0.0398 0.0807 1.01 0.193 0.119 0.41 0.1 10 20.1 0.157 0.241 1.01 0.104 0.101 0.0554 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS2036 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3000 ELBS3001 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S002 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS2036S003 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3000S001 ELBS3001S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:10 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 6/20/13 8:15 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/14/14 8:45 5/13/14 12:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Sample  Bottom  Depth (feet bgs) 6.5 6.5 6.5 6.5 6.5 6.5 6.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs Energetics Energetics Energetics Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Analysis  Method 6020 6020 6020 6020 6020 6020 6020 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8315A 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte Copper Lead Molybdenum Nickel Selenium Silver Thallium Aluminum Barium Beryllium Boron Chromium Cobalt Lithium Manganese Potassium Sodium Vanadium Zinc Zirconium Antimony Arsenic Cadmium Copper Lead Molybdenum Nickel Selenium Silver Thallium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Antimony Cadmium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Formaldehyde 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol Page 93 of 108 CAS Number 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7429905 7440393 7440417 7440428 7440473 7440484 7439932 7439965 7440097 7440235 7440622 7440666 7440677 7440360 7440382 7440439 7440508 7439921 7439987 7440020 7782492 7440224 7440280 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7440360 7440439 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 50000 121142 606202 98953 120821 122667 95954 88062 120832 105679 51285 Result  Value 13.6 8.9 0.501 16.4 0.162 0.0313 0.287 16600 84.9 0.728 2.47 22.3 9.66 24.7 291 2940 164 47.5 60.2 4.55 0.0903 9.59 0.112 10.2 6.47 0.374 14.2 0.105 0.0441 0.273 3.73 3.5 6.47 29.3 245 3.7 1.3 2.82 1.46 10.5 0.325 6.33 1.55 1.58 1.97 0.911 0.416 0.134 111 488 48.9 76.9 78.3 2790 22.9 14.7 37.9 4.48 0.122 0.751 18 18 18 18 18 18 18 99 18 1.8 1.8 4.5 0.88 0.88 1.1 18 0.88 2 1.8 0.88 1.8 1.8 1.8 1.9 0.88 0.88 0.88 1.8 7.1 35 2.2 180 35 35 35 35 35 35 35 35 1100 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 13.6 mg/kg 8.9 mg/kg 0.501 mg/kg 16.4 mg/kg 0.162 mg/kg 0.12 mg/kg 0.287 mg/kg 16600 mg/kg 84.9 mg/kg 0.728 mg/kg 5.25 mg/kg 22.3 mg/kg 9.66 mg/kg 24.7 mg/kg 291 mg/kg 2940 mg/kg 164 mg/kg 47.5 mg/kg 60.2 mg/kg 4.55 mg/kg 0.21 mg/kg 9.59 mg/kg 0.112 mg/kg 10.2 mg/kg 6.47 mg/kg 0.374 mg/kg 14.2 mg/kg 0.42 mg/kg 0.0441 mg/kg 0.273 mg/kg 0.00000373 mg/kg 0.0000035 mg/kg 0.00000647 mg/kg 0.0000293 mg/kg 0.000245 mg/kg 0.0000037 mg/kg 0.0000013 mg/kg 0.00000282 mg/kg 0.00000146 mg/kg 0.0000105 mg/kg 0.000000325 mg/kg 0.00000633 mg/kg 0.00000155 mg/kg 0.0000052 mg/kg 0.00000197 mg/kg 0.000000911 mg/kg 0.000000416 mg/kg 0.00000104 mg/kg 0.000111 mg/kg 0.000488 mg/kg 0.0000489 mg/kg 0.0000769 mg/kg 0.0000783 mg/kg 0.00279 mg/kg 0.0000229 mg/kg 0.0000147 mg/kg 0.0000379 mg/kg 0.00000448 mg/kg 0.122 mg/kg 0.751 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.099 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0045 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.0011 mg/kg 0.018 mg/kg 0.00088 mg/kg 0.002 mg/kg 0.0018 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0071 mg/kg 0.035 mg/kg 2.2 mg/kg 0.18 mg/kg 0.035 mg/kg 0.035 mg/kg 0.035 mg/kg 0.035 mg/kg 0.035 mg/kg 0.035 mg/kg 0.035 mg/kg 0.035 mg/kg 1.1 mg/kg Detected Y Y Y Y Y N Y Y Y Y N Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Project  Qual  Code Validation Note J J Q, Q, B Q, Q J J U Q, Q Q, Q U B J Q, Q Q J UJ Q, Q Q, Q J J Q, Q, B Q, Q J U J Q, Q J J J J $, F, F, B $, F, F, B , F, B , F, B , B , F, F J J UJ J J J U F , F, F , *DVR, F, F , F, B , F, F, B F $, F, F, B $, F, F, B J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 42 No 3.24E‐01 Background 33.9 No 2.63E‐01 Background 1.642 No 3.05E‐01 Background 64.2 No 2.55E‐01 Background 1 No 1.62E‐01 MRL 0.99 No 1.21E‐01 Ecological RBSL 0.761 No 3.77E‐01 Suburban Residential RBSL 37900 No 4.38E‐01 Background 203.8 No 4.17E‐01 Background 4.8 No 1.52E‐01 Ecological RBSL 22 No 2.39E‐01 Ecological RBSL 60.11 No 3.71E‐01 Background 26.18 No 3.69E‐01 Background 64.4 No 3.84E‐01 Background 723 No 4.02E‐01 Background 7524 No 3.91E‐01 Background 754 No 2.18E‐01 Background 111.8 No 4.25E‐01 Background 153 No 3.93E‐01 Background 10.64 No 4.28E‐01 Background 0.5 No 4.20E‐01 MRL 24.2 No 3.96E‐01 Background 0.435 No 2.57E‐01 Background 42 No 2.43E‐01 Background 33.9 No 1.91E‐01 Background 1.642 No 2.28E‐01 Background 64.2 No 2.21E‐01 Background 1 No 4.20E‐01 MRL 0.99 No 4.45E‐02 Ecological RBSL 0.761 No 3.59E‐01 Suburban Residential RBSL 0.0000057 No 6.54E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.15E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.5 No 2.44E‐01 MRL 0.435 Yes 1.73E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.50E‐01 Ecological RBSL 0.18 No 1.00E‐01 Ecological RBSL 0.082 No 2.20E‐01 Ecological RBSL 0.043 No 4.19E‐01 Ecological RBSL 0.017 Yes 1.06E+00 MRL 0.039 Yes 2.54E+00 Ecological RBSL 0.025 No 7.20E‐01 Ecological RBSL 0.0051 No 3.53E‐01 Ecological RBSL 0.004164 No 4.32E‐01 Background 0.006101 No 7.38E‐01 Background 0.0348 No 2.53E‐02 Suburban Residential RBSL 0.073 No 1.21E‐02 Ecological RBSL 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.31E‐02 Ecological RBSL 0.013 No 1.54E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 4.00E‐03 Ecological RBSL 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.17E‐02 Ecological RBSL 0.087 No 1.01E‐02 Ecological RBSL 0.0017 No 5.18E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.84E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 43 No 5.12E‐02 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 10 No 3.50E‐03 Ecological RBSL ‐‐ No SL No SL 75 No 4.67E‐04 Ecological RBSL 7.43 No 4.71E‐03 Suburban Residential RBSL ‐‐ No SL No SL 65 No 5.38E‐04 Ecological RBSL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 0.241 0.241 0.12 0.482 0.482 0.12 0.12 10.5 0.525 0.262 5.25 0.787 0.525 2.1 0.525 52.5 52.5 0.525 2.1 5.25 0.21 0.42 0.105 0.21 0.21 0.105 0.42 0.42 0.105 0.105 5.2 5.2 5.2 5.2 5.2 5.2 5.2 5.2 5.2 5.2 5.2 5.2 5.2 1.04 1.04 5.2 5.2 5.2 5.2 10.4 10.4 5.2 5.2 1.04 1.04 0.207 0.103 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.88 0.88 1.1 18 0.88 2 1.8 0.88 1.8 1.8 1.8 1.9 0.88 0.88 0.88 1.8 7.1 35 2.2 180 35 35 35 35 35 35 35 35 1100 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.116 0.0193 0.0602 0.0915 0.12 0.0313 0.0361 7.57 0.0346 0.0703 0.882 0.168 0.104 0.36 0.0871 8.75 17.5 0.136 0.21 0.882 0.0903 0.0882 0.0483 0.101 0.0168 0.0525 0.0798 0.105 0.0273 0.0315 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.128 0.217 0.179 0.238 0.225 0.211 0.229 0.216 0.233 0.12 0.206 0.208 0.12 0.21 0.134 0.149 0.217 0.218 0.229 0.114 0.201 0.12 0.206 0.21 0.134 0.0888 0.0475 3.5 3.5 3.8 4.9 8.5 3.5 3.5 3.5 5.2 0.35 1.5 0.35 0.35 0.18 0.32 4.2 0.19 2 0.35 0.23 0.35 0.52 0.35 0.35 0.18 0.32 0.2 0.35 1.8 12 1.3 71 18 18 18 18 18 18 18 18 320 MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S001 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:30 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Tentatively Identified Compound Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs Other SVOCs Energetics Energetics Energetics Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Analysis  Method 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C 8270C 8270C 8270C SIM 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzoic acid Benzyl alcohol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Carbazole Dibenzofuran Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine o‐Cresol p‐Chloroaniline p‐Chloro‐m‐cresol p‐Cresol Pentachlorophenol Phenol p‐Nitroaniline bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2‐Dichlorobenzene 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene 4‐Hydroxy‐4‐Methyl‐2‐pentanone 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine Page 94 of 108 CAS Number 91587 95578 88744 88755 91941 99092 534521 101553 7005723 100027 62533 65850 100516 111911 111444 108601 117817 85687 86748 132649 84662 131113 84742 117840 118741 87683 77474 67721 78591 62759 621647 86306 95487 106478 59507 106445 87865 108952 100016 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 95501 541731 106467 123422 121142 606202 98953 120821 122667 95954 88062 120832 105679 51285 91587 95578 88744 88755 91941 Result  Value 35 35 35 35 350 180 530 35 35 530 530 530 530 35 35 35 180 180 35 35 180 180 180 180 18 35 530 180 35 180 35 35 35 35 35 35 180 35 180 19 19 19 19 19 19 1.8 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 4 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 0.41 1.8 1.8 1.8 1.8 1.8 1.8 1.8 35 35 35 4600 190 37 37 37 37 37 37 37 37 1100 37 37 37 37 370 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.035 0.035 0.035 0.035 0.35 0.18 0.53 0.035 0.035 0.53 0.53 0.53 0.53 0.035 0.035 0.035 0.18 0.18 0.035 0.035 0.18 0.18 0.18 0.18 0.018 0.035 0.53 0.18 0.035 0.18 0.035 0.035 0.035 0.035 0.035 0.035 0.18 0.035 0.18 0.019 0.019 0.019 0.019 0.019 0.019 0.0018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.004 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.00041 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.035 0.035 0.035 4.6 0.19 0.037 0.037 0.037 0.037 0.037 0.037 0.037 0.037 1.1 0.037 0.037 0.037 0.037 0.37 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N Y N N N N N N N N N N Y N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U J U U U U U U U U U U T‐I U U U U U U U U U U U U U U U Validation Note Q F F T‐I Boeing Soil Char Level  (mg/kg) ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8 ‐‐ 4.5 4.5 ‐‐ ‐‐ ‐‐ 0.32 90 1.5 1.2 2.3 4.5 0.11 13 ‐‐ 0.022 3 ‐‐ ‐‐ 0.0325 ‐‐ 2.3 4.3 ‐‐ 1.7 4.3 2.8 5.1 3.4 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 130 23 1.33 ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ 75 7.43 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Exceeds Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL No No SL No No No SL No SL No SL No No No No No No Yes No No SL Yes No No SL No SL Yes No SL No No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No No SL No No No SL No No SL No SL No SL No SL No SL No SL Ratio Boeing Soil Char Level No SL No SL No SL No SL No SL No SL No SL No SL No SL 6.63E‐02 No SL 1.18E‐01 1.18E‐01 No SL No SL No SL 5.63E‐01 2.00E‐03 2.33E‐02 2.92E‐02 7.83E‐02 4.00E‐02 1.64E+00 1.38E‐02 No SL 1.59E+00 1.77E‐01 No SL No SL 5.54E+00 No SL 1.52E‐02 8.14E‐03 No SL 2.06E‐02 8.14E‐03 6.43E‐02 6.86E‐03 5.29E‐02 5.94E‐02 2.11E‐04 8.26E‐03 4.22E‐03 1.73E‐01 1.46E‐03 5.54E‐02 2.47E‐03 3.40E‐04 1.64E‐02 5.45E‐02 8.18E‐03 4.65E‐02 4.65E‐01 4.65E‐02 2.43E‐03 4.65E‐02 1.50E‐02 1.59E‐01 3.33E‐04 2.02E‐02 4.65E‐02 1.23E‐03 1.38E‐02 3.33E‐03 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 3.42E‐04 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 2.69E‐04 1.52E‐03 2.63E‐02 No SL No SL No SL No SL 3.70E‐03 No SL 4.93E‐04 4.98E‐03 No SL 5.69E‐04 No SL No SL No SL No SL No SL No SL SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 35 35 35 35 350 180 530 35 35 530 530 530 530 35 35 35 180 180 35 35 180 180 180 180 18 35 530 180 35 180 35 35 35 35 35 35 180 35 180 19 19 19 19 19 19 1.8 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 35 35 35 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 7 18 18 18 110 71 180 18 18 180 180 180 180 18 18 18 71 71 18 18 71 71 71 71 4 18 180 35 18 71 18 18 18 18 18 18 35 18 71 6.4 6.4 6.4 6.4 6.4 6.4 0.71 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.71 0.71 0.71 0.36 0.36 0.71 0.71 0.71 0.71 0.71 0.36 0.71 0.71 0.71 0.71 0.71 0.71 0.71 18 18 18 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 190 37 37 37 37 37 37 37 37 1100 37 37 37 37 370 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 75 19 19 19 19 19 19 19 19 340 8 19 19 19 110 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N N N N Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S002 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:40 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Tentatively Identified Compound Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs Other SVOCs Energetics Energetics Energetics Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Analysis  Method 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C 8270C 8270C 8270C SIM 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte 3,5‐Dimethylphenol 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Carbazole Dibenzofuran Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine o‐Cresol p‐Chloroaniline p‐Chloro‐m‐cresol p‐Cresol Pentachlorophenol Phenol p‐Nitroaniline bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2‐Dichlorobenzene 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene 4‐Hydroxy‐4‐Methyl‐2‐pentanone 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3,5‐Dimethylphenol 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol Page 95 of 108 CAS Number 108689 99092 534521 101553 7005723 100027 62533 92875 65850 100516 111911 111444 108601 117817 85687 86748 132649 84662 131113 84742 117840 118741 87683 77474 67721 78591 62759 621647 86306 95487 106478 59507 106445 87865 108952 100016 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 95501 541731 106467 123422 121142 606202 98953 120821 122667 95954 88062 120832 105679 51285 91587 95578 88744 88755 91941 108689 99092 534521 Result  Value 190 190 560 37 37 560 560 3700 560 560 37 37 37 190 190 37 37 190 190 190 190 19 37 560 190 37 190 37 37 37 37 37 37 190 37 190 20 20 20 20 20 20 1.8 19 19 19 19 19 4 19 19 19 19 19 19 19 19 19 19 19 4 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 37 37 37 780 190 39 39 39 39 39 39 39 39 1200 38 39 39 39 390 190 190 580 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units 0.19 0.19 0.56 0.037 0.037 0.56 0.56 3.7 0.56 0.56 0.037 0.037 0.037 0.19 0.19 0.037 0.037 0.19 0.19 0.19 0.19 0.019 0.037 0.56 0.19 0.037 0.19 0.037 0.037 0.037 0.037 0.037 0.037 0.19 0.037 0.19 0.02 0.02 0.02 0.02 0.02 0.02 0.0018 0.019 0.019 0.019 0.019 0.019 0.004 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.004 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.0018 0.037 0.037 0.037 0.78 0.19 0.039 0.039 0.039 0.039 0.039 0.039 0.039 0.039 1.2 0.038 0.039 0.039 0.039 0.39 0.19 0.19 0.58 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Project  Qual  Code N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U T‐I U U U U U U U U U U U U U U U U U U Validation Note F F T‐I Boeing Soil Char Level  (mg/kg) 2.6 ‐‐ ‐‐ ‐‐ ‐‐ 8 ‐‐ ‐‐ 4.5 4.5 ‐‐ ‐‐ ‐‐ 0.32 90 1.5 1.2 2.3 4.5 0.11 13 ‐‐ 0.022 3 ‐‐ ‐‐ 0.0325 ‐‐ 2.3 4.3 ‐‐ 1.7 4.3 2.8 5.1 3.4 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 130 23 1.33 ‐‐ ‐‐ ‐‐ ‐‐ 10 ‐‐ 75 7.43 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.6 ‐‐ ‐‐ Exceeds Boeing Soil Char Level No No SL No SL No SL No SL No No SL No SL No No No SL No SL No SL No No No No No No Yes No No SL Yes No No SL No SL Yes No SL No No No SL No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No SL No SL No SL No SL No No SL No No No SL No No SL No SL No SL No SL No SL No SL No No SL No SL Ratio Boeing Soil Char Level 7.31E‐02 No SL No SL No SL No SL 7.00E‐02 No SL No SL 1.24E‐01 1.24E‐01 No SL No SL No SL 5.94E‐01 2.11E‐03 2.47E‐02 3.08E‐02 8.26E‐02 4.22E‐02 1.73E+00 1.46E‐02 No SL 1.68E+00 1.87E‐01 No SL No SL 5.85E+00 No SL 1.61E‐02 8.60E‐03 No SL 2.18E‐02 8.60E‐03 6.79E‐02 7.25E‐03 5.59E‐02 6.25E‐02 2.22E‐04 8.70E‐03 4.44E‐03 1.82E‐01 1.54E‐03 5.54E‐02 2.61E‐03 3.58E‐04 1.73E‐02 5.76E‐02 8.64E‐03 1.03E‐02 4.91E‐01 4.91E‐02 2.57E‐03 4.91E‐02 1.58E‐02 1.68E‐01 3.52E‐04 2.13E‐02 4.91E‐02 1.30E‐03 1.46E‐02 3.33E‐03 2.47E‐04 3.40E‐05 1.64E‐03 5.45E‐03 8.18E‐04 4.65E‐03 4.65E‐02 4.65E‐03 2.43E‐04 4.65E‐03 1.50E‐03 1.59E‐02 3.33E‐05 2.02E‐03 4.65E‐03 1.23E‐04 1.38E‐03 1.50E‐03 2.85E‐04 1.61E‐03 2.78E‐02 No SL No SL No SL No SL 3.90E‐03 No SL 5.20E‐04 5.25E‐03 No SL 6.00E‐04 No SL No SL No SL No SL No SL No SL 7.31E‐02 No SL No SL SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 190 190 560 37 37 560 560 3700 560 560 37 37 37 190 190 37 37 190 190 190 190 19 37 560 190 37 190 37 37 37 37 37 37 190 37 190 20 20 20 20 20 20 1.8 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 19 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 37 37 37 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 37 75 190 19 19 190 190 780 190 190 19 19 19 75 75 19 19 75 75 75 75 4 19 190 37 19 75 19 19 19 19 19 19 37 19 75 6.6 6.6 6.6 6.6 6.6 6.6 0.74 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 0.74 0.74 0.74 0.37 0.37 0.74 0.74 0.74 0.74 0.74 0.37 0.74 0.74 0.74 0.74 0.74 0.74 0.74 19 19 19 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 190 39 39 39 39 39 39 39 39 1200 38 39 39 39 390 190 190 580 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 77 19 19 19 19 19 19 19 19 350 8 19 19 19 120 39 77 190 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N N N N Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N Y N N N N N N N N N N N Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3002 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3002S003 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/20/14 10:50 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Tentatively Identified Compound Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH VOCs VOCs VOCs Other SVOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Carbazole Dibenzofuran Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine o‐Cresol p‐Chloroaniline p‐Chloro‐m‐cresol p‐Cresol Pentachlorophenol Phenol p‐Nitroaniline 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2‐Dichlorobenzene 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene 4‐Hydroxy‐4‐Methyl‐2‐pentanone DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Antimony Cadmium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran Page 96 of 108 CAS Number 101553 7005723 100027 62533 92875 65850 100516 111911 111444 108601 117817 85687 86748 132649 84662 131113 84742 117840 118741 87683 77474 67721 78591 62759 621647 86306 95487 106478 59507 106445 87865 108952 100016 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 95501 541731 106467 123422 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7440360 7440439 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 Result  Value 39 39 580 580 3900 580 580 39 39 39 200 190 39 39 190 190 190 190 20 39 580 190 39 190 39 39 39 39 39 39 200 39 190 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 39 39 39 830 7.58 8.5 14.6 0.383 76.3 524 5.51 3.06 7.77 3.22 20.1 0.388 16.6 2.53 5.14 3.82 1.2 0.42 219 967 88.1 136 209 7060 24.2 25.7 12.3 5.36 0.244 0.298 19 19 19 19 19 19 19 19 46 13.7 13.4 20.3 75.3 601 5.15 4.87 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.039 mg/kg 0.039 mg/kg 0.58 mg/kg 0.58 mg/kg 3.9 mg/kg 0.58 mg/kg 0.58 mg/kg 0.039 mg/kg 0.039 mg/kg 0.039 mg/kg 0.2 mg/kg 0.19 mg/kg 0.039 mg/kg 0.039 mg/kg 0.19 mg/kg 0.19 mg/kg 0.19 mg/kg 0.19 mg/kg 0.02 mg/kg 0.039 mg/kg 0.58 mg/kg 0.19 mg/kg 0.039 mg/kg 0.19 mg/kg 0.039 mg/kg 0.039 mg/kg 0.039 mg/kg 0.039 mg/kg 0.039 mg/kg 0.039 mg/kg 0.2 mg/kg 0.039 mg/kg 0.19 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.039 mg/kg 0.039 mg/kg 0.039 mg/kg 0.83 mg/kg 0.00000758 mg/kg 0.0000085 mg/kg 0.0000146 mg/kg 0.000000383 mg/kg 0.0000763 mg/kg 0.000524 mg/kg 0.00000551 mg/kg 0.00000306 mg/kg 0.00000777 mg/kg 0.00000322 mg/kg 0.0000201 mg/kg 0.00000547 mg/kg 0.0000166 mg/kg 0.00000253 mg/kg 0.00000547 mg/kg 0.00000382 mg/kg 0.0000012 mg/kg 0.00000042 mg/kg 0.000219 mg/kg 0.000967 mg/kg 0.0000881 mg/kg 0.000136 mg/kg 0.000209 mg/kg 0.00706 mg/kg 0.0000242 mg/kg 0.0000257 mg/kg 0.0000123 mg/kg 0.00000536 mg/kg 0.244 mg/kg 0.298 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.046 mg/kg 0.0000137 mg/kg 0.0000134 mg/kg 0.0000203 mg/kg 0.0000753 mg/kg 0.000601 mg/kg 0.00000515 mg/kg 0.00000487 mg/kg Detected N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N Y Y Y Y Y Y Y Y Project  Qual  Code U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U T‐I Validation Note T‐I J J J UJ J UJ J J J , F, F, B , F, F, B , F, B , F, B , F, B , F, F, B , B , *DVR, F, B , F, B , F, F, B , *DVR, F, F, B , F, B , F, F, B J , F, F, B C, B J Q, Q U U U U U U U U F, F, B F, F F, B F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL 8 No 7.25E‐02 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 4.5 No 1.29E‐01 Ecological RBSL 4.5 No 1.29E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.32 No 6.25E‐01 Ecological RBSL 90 No 2.11E‐03 Ecological RBSL 1.5 No 2.60E‐02 Ecological RBSL 1.2 No 3.25E‐02 Ecological RBSL 2.3 No 8.26E‐02 Ecological RBSL 4.5 No 4.22E‐02 Ecological RBSL 0.11 Yes 1.73E+00 Ecological RBSL 13 No 1.46E‐02 Ecological RBSL ‐‐ No SL No SL 0.022 Yes 1.77E+00 Ecological RBSL 3 No 1.93E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.0325 Yes 5.85E+00 Suburban Residential RBSL ‐‐ No SL No SL 2.3 No 1.70E‐02 Ecological RBSL 4.3 No 9.07E‐03 Ecological RBSL ‐‐ No SL No SL 1.7 No 2.29E‐02 Ecological RBSL 4.3 No 9.07E‐03 Ecological RBSL 2.8 No 7.14E‐02 Ecological RBSL 5.1 No 7.65E‐03 Ecological RBSL 3.4 No 5.59E‐02 Ecological RBSL 7.29 No 2.74E‐03 Suburban Residential RBSL 53 No 3.77E‐04 Ecological RBSL 1.1 No 1.82E‐02 Ecological RBSL 0.33 No 6.06E‐02 Ecological RBSL 2.2 No 9.09E‐03 Ecological RBSL 0.387 No 5.17E‐02 Suburban Residential RBSL 0.0387 No 5.17E‐01 Suburban Residential RBSL 0.387 No 5.17E‐02 Suburban Residential RBSL 7.4 No 2.70E‐03 Ecological RBSL 0.387 No 5.17E‐02 Suburban Residential RBSL 1.2 No 1.67E‐02 Ecological RBSL 0.113 No 1.77E‐01 Suburban Residential RBSL 54 No 3.70E‐04 Ecological RBSL 0.89 No 2.25E‐02 Ecological RBSL 0.387 No 5.17E‐02 Suburban Residential RBSL 14.6 No 1.37E‐03 Suburban Residential RBSL 1.3 No 1.54E‐02 Ecological RBSL 1.2 No 1.67E‐02 Ecological RBSL 130 No 3.00E‐04 Ecological RBSL 23 No 1.70E‐03 Ecological RBSL 1.33 No 2.93E‐02 Suburban Residential RBSL ‐‐ No SL No SL 0.0000057 Yes 1.33E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 2.59E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.5 No 4.88E‐01 MRL 0.435 No 6.85E‐01 Background ‐‐ No SL No SL No SL ‐‐ No SL 0.12 No 1.58E‐01 Ecological RBSL 0.18 No 1.06E‐01 Ecological RBSL 0.082 No 2.32E‐01 Ecological RBSL 0.043 No 4.42E‐01 Ecological RBSL 0.017 Yes 1.12E+00 MRL 0.039 No 4.87E‐01 Ecological RBSL 0.025 Yes 1.84E+00 Ecological RBSL 0.0000057 Yes 2.40E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 3.61E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 39 39 580 580 3900 580 580 39 39 39 200 190 39 39 190 190 190 190 20 39 580 190 39 190 39 39 39 39 39 39 200 39 190 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 20 39 39 39 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 19 19 190 190 810 190 190 19 19 19 77 77 19 19 77 77 77 77 4 19 190 39 19 77 19 19 19 19 19 19 39 19 77 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 19 19 19 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1.09 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 5.47 1.09 5.47 5.47 5.47 5.47 10.9 10.9 5.47 5.47 1.09 1.09 0.22 0.11 19 19 19 19 19 19 19 19 19 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0773 0.0373 0.135 0.0463 0.0697 0.0584 0.0689 0.0616 0.0662 0.0639 0.0376 0.0941 0.0669 0.0387 0.0479 0.0413 0.135 0.0678 0.0612 0.029 0.0859 0.0381 0.0941 0.0605 0.0479 0.0944 0.0505 3.7 3.7 4 5.2 9 3.7 3.7 3.7 5.5 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 4.82 4.82 4.82 4.82 ng/kg ng/kg ng/kg ng/kg 0.901 4.71 1.45 0.558 ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y N Y N N Y Y N Y N N Y Y Y N N N Y Y N N N N N Y N N N N N N N N N Y Y Y Y N Y N Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3004 ELBS3005 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3006 ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S001SP ELBS3003S002 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S003 ELBS3003S004 ELBS3004S001 ELBS3005S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3006S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 ELBS3003S001 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:30 5/13/14 9:45 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:00 5/13/14 10:15 5/13/14 11:15 5/13/14 13:45 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 5/14/14 8:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9 0.5 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 10 1.5 1.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6010B 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 7199 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6020 6020 8082 8082 8082 8082 8082 8082 8082 8082 8082 6020 7199 7199 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Antimony Cadmium Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1262 Hexavalent Chromium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Antimony Cadmium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Antimony Hexavalent Chromium Hexavalent Chromium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Page 97 of 108 CAS Number 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 51207319 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 7440360 7440439 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 18540299 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7440360 7440439 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 7440360 18540299 18540299 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 Result  Value 8.23 2.86 18.1 1.18 14.6 10.2 4.84 3.56 0.93 0.461 2.29 202 9300 1240 243 106 106 28.6 63.1 6.65 29.1 0.364 0.334 3.73 3.73 3.73 3.73 3.73 3.73 19.8 29.6 3.73 0.84 0.015 0.0494 0.0864 0.595 4.71 0.0822 0.0487 0.0765 0.051 0.175 0.0676 0.0976 0.0101 0.0516 0.0615 0.0283 0.0181 0.0257 1.59 9.39 0.948 1.23 1.55 47.1 6.01 6.01 1.2 1.2 0.13 0.0774 21 21 21 21 21 21 21 21 21 0.172 1.1 1.6 2.16 1.88 3.49 10.6 82.1 0.537 0.521 1.59 0.619 3 0.176 3.18 0.102 1.27 0.815 0.0975 0.157 0.203 23 172 13.9 24.1 25 1580 3.65 3.18 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.00000823 mg/kg 0.00000286 mg/kg 0.0000181 mg/kg 0.00000482 mg/kg 0.0000146 mg/kg 0.0000102 mg/kg 0.00000484 mg/kg 0.00000356 mg/kg 0.00000482 mg/kg 0.000000965 mg/kg 0.00000229 mg/kg 0.000202 mg/kg 0.0093 mg/kg 0.00124 mg/kg 0.000243 mg/kg 0.000106 mg/kg 0.000106 mg/kg 0.0000286 mg/kg 0.0000631 mg/kg 0.00000665 mg/kg 0.0000291 mg/kg 1.1 mg/kg 0.334 mg/kg 0.00373 mg/kg 0.00373 mg/kg 0.00373 mg/kg 0.00373 mg/kg 0.00373 mg/kg 0.00373 mg/kg 0.0198 mg/kg 0.0296 mg/kg 0.00373 mg/kg 0.84 mg/kg 0.000000015 mg/kg 4.94E‐08 mg/kg 8.64E‐08 mg/kg 0.00000601 mg/kg 0.00000471 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 7.65E‐08 mg/kg 0.00000601 mg/kg 0.000000175 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.0000012 mg/kg 0.0000012 mg/kg 0.00000159 mg/kg 0.00000939 mg/kg 0.000000948 mg/kg 0.00000123 mg/kg 0.000012 mg/kg 0.0000471 mg/kg 0.00000601 mg/kg 0.00000601 mg/kg 0.0000012 mg/kg 0.0000012 mg/kg 0.13 mg/kg 0.0774 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.172 mg/kg 1.1 mg/kg 1.6 mg/kg 0.00000216 mg/kg 0.00000188 mg/kg 0.00000349 mg/kg 0.0000106 mg/kg 0.0000821 mg/kg 0.00000557 mg/kg 0.000000521 mg/kg 0.00000557 mg/kg 0.000000619 mg/kg 0.000003 mg/kg 0.00000557 mg/kg 0.00000318 mg/kg 0.00000557 mg/kg 0.00000127 mg/kg 0.000000815 mg/kg 0.00000557 mg/kg 0.00000111 mg/kg 0.00000111 mg/kg 0.000023 mg/kg 0.000172 mg/kg 0.0000139 mg/kg 0.0000241 mg/kg 0.000025 mg/kg 0.00158 mg/kg 0.00000365 mg/kg 0.00000318 mg/kg Detected Y Y Y N Y Y Y Y N N Y Y Y Y Y Y Y Y Y Y Y N Y N N N N N N Y Y N Y Y Y Y N Y N N Y N Y N N N N N N N N Y Y Y Y N Y Y Y Y Y Y Y N N N N N N N N N Y Y Y Y Y Y Y Y N Y N Y Y N Y N Y Y N N N Y Y Y Y Y Y Y Y Project  Qual  Code J U J U U J Validation Note F, B F, F, B B F, B F, B F, F, B F, F, B F, B F, F, B B B F, F C, B U U U U U U U J *DVR U UJ J U U J UJ J UJ UJ U UJ UJ UJ U U J J J UJ J J J J J J U U U U U U U U U J UJ J UJ J J U J U J J U U U , *DVR, F, F, B , F, F, B , F, B , F, B , F, B , *DVR, F, F, B , B , *DVR, F, B , *DVR, F, B F, F, B , *DVR, F, F, B , *DVR, F, B , *DVR, F, F, B , *DVR, F, F, B , F, F, B , Original Result = 0.401 , Original Result = 0.487 , Original Result = 0.146 , Original Result = 0.0279 Q, Q Q, Q, Q, Q $, F, F, B $, F, F, B , *DVR, F, B , F, B , *DVR, B , F, F , F F, F , F, F , F, B F, F, B F $, F, F, B $, F, F, B J J Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.5 Yes 2.20E+00 MRL 0.435 No 7.68E‐01 Background ‐‐ No SL No SL 0.12 No 3.11E‐02 Ecological RBSL 0.18 No 2.07E‐02 Ecological RBSL 0.082 No 4.55E‐02 Ecological RBSL 0.043 No 8.67E‐02 Ecological RBSL 0.017 No 2.19E‐01 MRL 0.039 No 5.08E‐01 Ecological RBSL 0.025 Yes 1.18E+00 Ecological RBSL ‐‐ No SL No SL 1.29 No 6.51E‐01 Suburban Residential RBSL 0.0000057 No 2.63E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 1.53E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.5 No 2.60E‐01 MRL 0.435 No 1.78E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.75E‐01 Ecological RBSL 0.18 No 1.17E‐01 Ecological RBSL 0.082 No 2.56E‐01 Ecological RBSL 0.043 No 4.88E‐01 Ecological RBSL 0.017 Yes 1.24E+00 MRL 0.039 No 5.38E‐01 Ecological RBSL 0.025 No 8.40E‐01 Ecological RBSL 0.5 No 3.44E‐01 MRL 1.29 No 8.53E‐01 Suburban Residential RBSL 1.29 Yes 1.24E+00 Suburban Residential RBSL 0.0000057 No 3.79E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 6.20E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 4.82 4.82 4.82 4.82 4.82 4.82 4.82 4.82 4.82 0.965 0.965 9.65 9.65 4.82 4.82 4.82 4.82 4.82 4.82 0.965 0.965 1.1 0.214 3.73 3.73 3.73 3.73 3.73 3.73 3.73 3.73 3.73 0.43 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 1.26 0.521 1.26 1 1.33 0.586 0.55 0.594 0.536 0.222 0.477 1.05 5.96 4.71 0.901 1.26 0.521 0.55 0.126 0.222 0.477 0.364 0.0214 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 1.24 0.15 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 6.01 1.2 1.2 6.01 6.01 6.01 6.01 12 12 6.01 6.01 1.2 1.2 0.249 0.124 21 21 21 21 21 21 21 21 21 0.235 0.53 0.48 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg 0.0135 0.0274 0.0297 0.0233 0.0242 0.02 0.025 0.0254 0.0247 0.0101 0.0226 0.0212 0.0111 0.0181 0.0257 0.0185 0.0274 0.0223 0.0247 0.0196 0.021 0.0106 0.0226 0.0181 0.0257 0.107 0.0572 4.1 4.1 4.5 5.7 10 4.1 4.1 4.1 6.1 0.101 0.19 0.17 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg 5.57 5.57 5.57 5.57 5.57 5.57 5.57 5.57 5.57 5.57 5.57 5.57 5.57 1.11 1.11 5.57 5.57 5.57 5.57 11.1 11.1 5.57 5.57 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.118 0.26 0.161 0.173 0.267 0.159 0.258 0.176 0.243 0.102 0.142 0.163 0.0975 0.157 0.203 0.136 0.26 0.167 0.256 0.153 0.23 0.0999 0.142 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N Y Y N N N Y N Y Y Y N Y Y Y Y Y N Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3006 ELBS3006 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3006S001 ELBS3006S001 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007D003 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S001 ELBS3007S002 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 Sample ID Sample Type Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date Matrix  Type 5/14/14 8:30 5/14/14 8:30 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:30 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6010B 7199 8082 8082 8082 8082 8082 8082 8082 8082 8082 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6010B 8082 8082 8082 8082 8082 8082 8082 8082 8082 7199 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Manganese Hexavalent Chromium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Manganese Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Hexavalent Chromium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Page 98 of 108 CAS Number 55722275 41903575 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7439965 18540299 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7439965 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 18540299 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 Result  Value 1.11 1.11 0.191 0.0981 0.076 0.0527 0.232 1.33 0.0459 0.0538 0.0161 0.0527 0.0829 0.0143 0.0639 0.208 0.0231 0.0751 0.165 0.02 0.608 2.97 0.817 5.83 0.588 15 1.69 5.83 1.32 1.17 163 0.42 20 20 20 20 20 20 20 12 20 0.000651 0.000651 0.00447 0.0722 0.36 0.0643 0.0472 0.0283 0.04 0.0601 0.0893 0.0705 0.0774 0.0306 0.0372 0.0312 0.0141 0.0225 5.48 0.713 5.48 5.48 0.226 2.91 5.48 5.48 1.1 1.1 267 19 19 19 19 19 19 19 33 19 0.88 0.00131 0.00131 0.00844 0.0419 0.105 0.646 0.0443 0.0426 0.0282 0.0174 0.0286 0.029 0.0296 0.0889 0.0311 0.00889 0.031 0.018 5.91 1.36 5.91 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.00000111 mg/kg 0.00000111 mg/kg 0.000000191 mg/kg 9.81E‐08 mg/kg 0.000000076 mg/kg 0.00000117 mg/kg 0.000000232 mg/kg 0.00000133 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.000000208 mg/kg 0.00000583 mg/kg 0.00000583 mg/kg 0.000000165 mg/kg 0.00000117 mg/kg 0.000000608 mg/kg 0.00000297 mg/kg 0.000000817 mg/kg 0.00000583 mg/kg 0.000000588 mg/kg 0.000015 mg/kg 0.00000169 mg/kg 0.00000583 mg/kg 0.00000132 mg/kg 0.00000117 mg/kg 163 mg/kg 0.42 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.012 mg/kg 0.02 mg/kg 6.51E‐10 mg/kg 6.51E‐10 mg/kg 4.47E‐09 mg/kg 0.00000548 mg/kg 0.00000036 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.0000011 mg/kg 0.0000011 mg/kg 0.00000548 mg/kg 0.000000713 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.000011 mg/kg 0.00000291 mg/kg 0.00000548 mg/kg 0.00000548 mg/kg 0.0000011 mg/kg 0.0000011 mg/kg 267 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.019 mg/kg 0.033 mg/kg 0.019 mg/kg 0.88 mg/kg 1.31E‐09 mg/kg 1.31E‐09 mg/kg 8.44E‐09 mg/kg 0.00000118 mg/kg 0.00000591 mg/kg 0.000000646 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000118 mg/kg 0.00000591 mg/kg 0.00000136 mg/kg 0.00000591 mg/kg Detected Y Y Y Y Y N Y Y N N N N N N N Y N N Y N Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N Y Y Y N Y N N N N N N N N N N N N N Y Y Y Y N Y Y Y Y Y Y N N N N N N N Y N Y Y Y Y N N Y N N N N N N N N N N N N Y Y Y Project  Qual  Code Validation Note J J , Original Result = 0.701 , Original Result = 0.982 UJ J J U UJ U UJ UJ UJ UJ J UJ U J U J J J J J , *DVR , F, F, B , F, F, B , F, B , *DVR, F, B F, B , *DVR, F, F, B , *DVR, F, B *DVR, F, B , *DVR, F, B , F, F, B , *DVR, F, F, B , F, B , F, F, B , Original Result = 0.661 , F, F, B , F, F, B J J , Original Result = 0.462 J , Original Result = 0.119 J U U U U U U U J U UJ J UJ UJ UJ UJ UJ UJ U UJ UJ U U U UJ J J J J U J J J J J , *DVR, F, F, B , F, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, F, B , *DVR, F, B , *DVR, F, B , F, B , *DVR, F, F, B , *DVR, F, F, B , F, B , F, F, B , *DVR , Original Result = 0.199 , Original Result = 0.292 , Original Result = 0.455 , F, F, B , F, F, B , Original Result = 0.254 , Original Result = 0.198 , Original Result = 0.137 , Original Result = 0.207 U U U U U U U U U UJ J UJ UJ UJ UJ U U UJ U UJ U UJ U J J J , *DVR, F, F, B , F, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, F, B , F, B , F, B , *DVR, F, B , F, F, B , *DVR, F, F, B F, B , *DVR, F, F, B , Original Result = 0.269 , Original Result = 0.252 Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL 0.0000057 No 3.35E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 1.35E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 723 No 2.25E‐01 Background 1.29 No 3.26E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.67E‐01 Ecological RBSL 0.18 No 1.11E‐01 Ecological RBSL 0.082 No 2.44E‐01 Ecological RBSL 0.043 No 4.65E‐01 Ecological RBSL 0.017 Yes 1.18E+00 MRL 0.039 No 3.08E‐01 Ecological RBSL 0.025 No 8.00E‐01 Ecological RBSL 0.0000057 No 1.14E‐04 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 7.94E‐03 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 723 No 3.69E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.58E‐01 Ecological RBSL 0.18 No 1.06E‐01 Ecological RBSL 0.082 No 2.32E‐01 Ecological RBSL 0.043 No 4.42E‐01 Ecological RBSL 0.017 Yes 1.12E+00 MRL 0.039 No 8.46E‐01 Ecological RBSL 0.025 No 7.60E‐01 Ecological RBSL 1.29 No 6.82E‐01 Suburban Residential RBSL 0.0000057 No 2.30E‐04 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 1.50E‐02 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 1.11 ng/kg 1.11 ng/kg MDL MDL  Units 0.157 ng/kg 0.203 ng/kg 1.17 5.83 5.83 5.83 5.83 5.83 5.83 5.83 5.83 5.83 5.83 5.83 5.83 5.83 1.17 5.83 5.83 5.83 5.83 11.7 11.7 5.83 5.83 1.17 1.17 0.578 0.48 20 20 20 20 20 20 20 20 20 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0425 0.0073 0.0163 0.0112 0.0148 0.0161 0.0131 0.0157 0.0143 0.0155 0.0144 0.0227 0.0136 0.0147 0.02 0.00881 0.0163 0.0139 0.0158 0.0159 0.0168 0.0145 0.0227 0.0201 0.02 0.0959 0.17 4 4 4.3 5.5 9.6 4 4 4 5.9 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.48 5.48 5.48 5.48 5.48 5.48 5.48 5.48 5.48 5.48 5.48 5.48 5.48 1.1 1.1 5.48 5.48 5.48 5.48 11 11 5.48 5.48 1.1 1.1 0.541 19 19 19 19 19 19 19 19 19 0.47 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.00599 0.0161 0.0109 0.0107 0.0133 0.00952 0.0138 0.012 0.0136 0.00842 0.0138 0.00991 0.00912 0.0141 0.0167 0.00772 0.0161 0.0105 0.0136 0.0177 0.0181 0.00875 0.0138 0.0141 0.0167 0.0899 3.7 3.7 4.1 5.2 9 3.7 3.7 3.7 5.5 0.16 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 1.18 5.91 5.91 5.91 5.91 5.91 5.91 5.91 5.91 5.91 5.91 5.91 5.91 5.91 1.18 5.91 5.91 5.91 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0419 0.00595 0.0157 0.0109 0.00964 0.0131 0.00837 0.0137 0.0103 0.0133 0.00884 0.0181 0.00889 0.0093 0.018 0.00767 0.0157 0.00924 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y N Y N N N N Y Y N Y N N Y N N Y Y N N Y N N Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N Y N N N Y N Y Y Y Y N N Y N Y Y N Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3008 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3007S003 ELBS3008S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S001 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 11:00 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:30 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9.2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 9.8 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6010B 7199 8082 8082 8082 8082 8082 8082 8082 8082 8082 6010B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6010B 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Manganese Hexavalent Chromium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Manganese DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Manganese Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Page 99 of 108 CAS Number 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7439965 18540299 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 7439965 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7439965 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 Result  Value 5.91 0.381 6.6 5.91 5.91 1.18 1.18 176 0.18 21 21 21 21 21 21 21 18 21 167 0.0643 0.102 0.208 0.651 6.99 0.0428 0.0579 0.0841 0.0571 0.497 0.257 0.444 0.107 0.0851 0.0463 0.0298 0.0155 0.0186 1.59 14.8 1.03 2.75 2.28 157 5.67 0.531 0.393 1.13 367 20 20 20 20 20 20 20 20 20 2 2 2 0.96 0.96 1.2 20 0.96 2 2 0.96 2 2 2 2.1 0.96 0.96 0.96 2 7.7 38 1 1.18 2.04 11.7 62.1 0.776 0.383 0.673 0.246 2.04 0.0955 1.34 0.0494 0.349 0.369 0.00989 0.0125 0.0439 28.5 135 9.65 14.1 45.2 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.00000591 mg/kg 0.0000118 mg/kg 0.0000066 mg/kg 0.00000591 mg/kg 0.00000591 mg/kg 0.00000118 mg/kg 0.00000118 mg/kg 176 mg/kg 0.5 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.018 mg/kg 0.021 mg/kg 167 mg/kg 6.43E‐08 mg/kg 0.000000102 mg/kg 0.000000208 mg/kg 0.000000651 mg/kg 0.00000699 mg/kg 0.00000567 mg/kg 0.00000567 mg/kg 8.41E‐08 mg/kg 0.00000567 mg/kg 0.000000497 mg/kg 0.000000257 mg/kg 0.00000567 mg/kg 0.00000567 mg/kg 0.00000567 mg/kg 0.00000567 mg/kg 0.00000567 mg/kg 0.00000113 mg/kg 0.00000113 mg/kg 0.00000159 mg/kg 0.0000148 mg/kg 0.00000103 mg/kg 0.00000275 mg/kg 0.00000228 mg/kg 0.000157 mg/kg 0.00000567 mg/kg 0.000000531 mg/kg 0.000000393 mg/kg 0.00000113 mg/kg 367 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00096 mg/kg 0.00096 mg/kg 0.0012 mg/kg 0.02 mg/kg 0.00096 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00096 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.0021 mg/kg 0.00096 mg/kg 0.00096 mg/kg 0.00096 mg/kg 0.002 mg/kg 0.0077 mg/kg 0.038 mg/kg 0.000001 mg/kg 0.00000118 mg/kg 0.00000204 mg/kg 0.0000117 mg/kg 0.0000621 mg/kg 0.000000776 mg/kg 0.000000383 mg/kg 0.000000673 mg/kg 0.000000246 mg/kg 0.00000204 mg/kg 0.00000511 mg/kg 0.00000134 mg/kg 0.00000511 mg/kg 0.000000349 mg/kg 0.000000369 mg/kg 0.00000511 mg/kg 0.00000102 mg/kg 4.39E‐08 mg/kg 0.0000285 mg/kg 0.000135 mg/kg 0.00000965 mg/kg 0.0000141 mg/kg 0.0000452 mg/kg Detected Y N Y Y Y Y Y Y N N N N N N N N Y N Y Y Y Y Y Y N N Y N Y Y N N N N N N N Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y N Y N Y Y N N Y Y Y Y Y Y Project  Qual  Code J UJ J J J J J Validation Note , Original Result = 0.471 , *DVR, F, F, B , F, F, B , Original Result = 0.357 , Original Result = 0.24 , Original Result = 0.234 , Original Result = 0.128 U U U U U U U U J U J U UJ J U J J UJ UJ UJ U UJ U U J J J J J J J J , F, F, B , F, F, B , F, B , *DVR, F, B , F, B , F, F, B , F, B , F, B , *DVR, F, B , *DVR, F, F, B , *DVR, F, F, B , F, B , *DVR, F, F, B , F, F, B , F, F, B , Original Result = 0.365 , Original Result = 0.123 U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J J J J J UJ J UJ J J U U J , F, F, B , F, F, B , F, B , F, B , F, B , F, F, B , F, B , *DVR, F, B , F, B , *DVR, F, F, B , F, F, B , F, B F, F, B , F, F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 723 No 2.43E‐01 Background 1.29 No 3.88E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.75E‐01 Ecological RBSL 0.18 No 1.17E‐01 Ecological RBSL 0.082 No 2.56E‐01 Ecological RBSL 0.043 No 4.88E‐01 Ecological RBSL 0.017 Yes 1.24E+00 MRL 0.039 No 4.62E‐01 Ecological RBSL 0.025 No 8.40E‐01 Ecological RBSL 723 No 2.31E‐01 Background 0.0000057 No 1.13E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 3.69E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 723 No 5.08E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.67E‐01 Ecological RBSL 0.18 No 1.11E‐01 Ecological RBSL 0.082 No 2.44E‐01 Ecological RBSL 0.043 No 4.65E‐01 Ecological RBSL 0.017 Yes 1.18E+00 MRL 0.039 No 5.13E‐01 Ecological RBSL 0.025 No 8.00E‐01 Ecological RBSL 0.0051 No 3.92E‐01 Ecological RBSL 0.004164 No 4.80E‐01 Background 0.006101 No 3.28E‐01 Background 0.0348 No 2.76E‐02 Suburban Residential RBSL 0.073 No 1.32E‐02 Ecological RBSL 0.394 No 3.05E‐03 Suburban Residential RBSL 1.1 No 1.82E‐02 Ecological RBSL 0.067 No 1.43E‐02 Ecological RBSL 0.013 No 1.54E‐01 Ecological RBSL 0.23 No 8.70E‐03 Ecological RBSL 0.22 No 4.36E‐03 Ecological RBSL 0.22 No 9.09E‐03 Ecological RBSL 0.0079 No 2.53E‐01 Ecological RBSL 0.0092 No 2.17E‐01 Ecological RBSL 0.0086 No 2.44E‐01 Ecological RBSL 0.075 No 1.28E‐02 Ecological RBSL 0.087 No 1.10E‐02 Ecological RBSL 0.0017 No 5.65E‐01 MRL 0.0328 No 6.10E‐02 Suburban Residential RBSL 2.5 No 3.08E‐03 Ecological RBSL 0.493 No 7.71E‐02 Suburban Residential RBSL 0.0000057 No 1.75E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 3.62E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 5.91 11.8 11.8 5.91 5.91 1.18 1.18 0.594 0.5 21 21 21 21 21 21 21 21 21 0.546 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg MDL 0.0134 0.017 0.0176 0.00906 0.0181 0.0158 0.018 0.0986 0.18 4 4 4.4 5.6 9.7 4 4 4 6 0.0906 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 5.67 1.13 1.13 5.67 5.67 5.67 5.67 11.3 11.3 5.67 5.67 1.13 1.13 0.572 20 20 20 20 20 20 20 20 20 2 2 2 0.96 0.96 1.2 20 0.96 2 2 0.96 2 2 2 2.1 0.96 0.96 0.96 2 7.7 38 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0107 0.0261 0.0187 0.0186 0.0253 0.0165 0.0264 0.02 0.0262 0.00769 0.021 0.0174 0.00761 0.0155 0.0186 0.0136 0.0261 0.018 0.026 0.0166 0.0248 0.00765 0.021 0.0155 0.0186 0.0949 3.8 3.8 4.1 5.3 9.2 3.8 3.8 3.8 5.6 0.38 0.38 0.38 0.38 0.2 0.35 4.6 0.21 0.38 0.38 0.25 0.38 0.38 0.38 0.38 0.2 0.35 0.22 0.38 2 13 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 5.11 5.11 5.11 5.11 5.11 5.11 5.11 5.11 5.11 5.11 5.11 5.11 5.11 1.02 1.02 5.11 5.11 5.11 5.11 10.2 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0151 0.0603 0.029 0.0272 0.0363 0.0233 0.0359 0.0299 0.034 0.00954 0.0245 0.0242 0.00989 0.0125 0.0172 0.0199 0.0603 0.0259 0.0354 0.0277 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y Y N Y Y N N N N N N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3009 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3010 ELBS3011 ELBS3011 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3009S002 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S001 ELBS3010S002 ELBS3011S001 ELBS3011S002 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/13/14 13:45 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:00 5/20/14 10:15 5/13/14 10:00 5/13/14 10:15 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals Metals VOCs VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans PCBs PCBs PCBs PCBs Analysis  Method 1613B 1613B 1613B 1613B 1613B 6010B 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6020 6020 7199 8315A 8315A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8082 8082 8082 8082 Analyte Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Manganese Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Arsenic Copper Hexavalent Chromium Formaldehyde Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Page 100 of 108 CAS Number 3268879 30402154 36088229 55722275 41903575 7439965 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7440382 7440508 18540299 50000 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 37324235 11100144 12674112 11104282 Result  Value 1280 1.34 1.58 0.332 1.02 244 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.89 0.89 1.1 18 0.89 1.8 1.8 0.89 1.8 1.8 1.8 1.9 0.89 0.89 0.89 1.8 7.1 35 8.98 10.1 13.6 0.115 60.1 332 3.47 2.34 6.34 3.14 11.6 0.0834 14.9 0.98 3.81 4.36 0.744 0.509 130 674 77.4 93.8 121 4380 20.7 13.9 7.73 1.65 22.2 15.5 0.17 2.3 2.3 20.1 20.7 29.4 167 825 10.4 7.03 12.2 7.73 23.3 0.29 23.3 1.82 5.74 10.9 2.81 1.31 0.437 366 1520 207 179 401 12100 47.4 26.4 21.8 1.92 18 18 18 18 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.00128 mg/kg 0.00000134 mg/kg 0.00000158 mg/kg 0.000000332 mg/kg 0.00000102 mg/kg 244 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00089 mg/kg 0.00089 mg/kg 0.0011 mg/kg 0.018 mg/kg 0.00089 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00089 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00089 mg/kg 0.00089 mg/kg 0.00089 mg/kg 0.0018 mg/kg 0.0071 mg/kg 0.035 mg/kg 0.00000898 mg/kg 0.0000101 mg/kg 0.0000136 mg/kg 0.00000119 mg/kg 0.0000601 mg/kg 0.000332 mg/kg 0.00000347 mg/kg 0.00000234 mg/kg 0.00000634 mg/kg 0.00000314 mg/kg 0.0000116 mg/kg 0.00000593 mg/kg 0.0000149 mg/kg 0.00000098 mg/kg 0.00000381 mg/kg 0.00000436 mg/kg 0.000000744 mg/kg 0.00000119 mg/kg 0.00013 mg/kg 0.000674 mg/kg 0.0000774 mg/kg 0.0000938 mg/kg 0.000121 mg/kg 0.00438 mg/kg 0.0000207 mg/kg 0.0000139 mg/kg 0.00000773 mg/kg 0.00000165 mg/kg 22.2 mg/kg 15.5 mg/kg 0.48 mg/kg 2.3 mg/kg 2.3 mg/kg 0.0000201 mg/kg 0.0000207 mg/kg 0.0000294 mg/kg 0.000167 mg/kg 0.000825 mg/kg 0.0000104 mg/kg 0.00000703 mg/kg 0.0000122 mg/kg 0.00000773 mg/kg 0.0000233 mg/kg 0.00000501 mg/kg 0.0000233 mg/kg 0.00000182 mg/kg 0.00000574 mg/kg 0.0000109 mg/kg 0.00000281 mg/kg 0.00000131 mg/kg 0.000000437 mg/kg 0.000366 mg/kg 0.00152 mg/kg 0.000207 mg/kg 0.000179 mg/kg 0.000401 mg/kg 0.0121 mg/kg 0.0000474 mg/kg 0.0000264 mg/kg 0.0000218 mg/kg 0.00000192 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg Detected Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y Y Y Y Y N Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y N N N Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Project  Qual  Code Validation Note , F, F, B J J J J , Original Result = 0.295 U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J J J U J J J J UJ $, F, F, B $, F, F, B , F, F, B , F, F, B , B $, F, B F, B $, B , F, F, B , F , F, F, B , F, F, B , *DVR, B $, F, F, B $, F, F, B B U U U U J J , F, F, B , F, F, B , F, B , F, B , F, B , F, F, B , F, B F, B , F, B , F, F, B , F, F, B , F, B , F, F, B J J U U U U , F, F, B C, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL 723 No 3.37E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.50E‐01 Ecological RBSL 0.18 No 1.00E‐01 Ecological RBSL 0.082 No 2.20E‐01 Ecological RBSL 0.043 No 4.19E‐01 Ecological RBSL 0.017 Yes 1.06E+00 MRL 0.039 No 4.62E‐01 Ecological RBSL 0.025 No 7.20E‐01 Ecological RBSL 0.0051 No 3.53E‐01 Ecological RBSL 0.004164 No 4.32E‐01 Background 0.006101 No 2.95E‐01 Background 0.0348 No 2.56E‐02 Suburban Residential RBSL 0.073 No 1.22E‐02 Ecological RBSL 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.33E‐02 Ecological RBSL 0.013 No 1.38E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 4.05E‐03 Ecological RBSL 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.19E‐02 Ecological RBSL 0.087 No 1.02E‐02 Ecological RBSL 0.0017 No 5.24E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.84E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 0.0000057 Yes 1.58E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 2.42E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 24.2 No 9.17E‐01 Background 42 No 3.69E‐01 Background 1.29 No 3.72E‐01 Suburban Residential RBSL 43 No 5.35E‐02 Ecological RBSL 43 No 5.35E‐02 Ecological RBSL 0.0000057 Yes 3.53E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 5.22E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.50E‐01 Ecological RBSL 0.18 No 1.00E‐01 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 10.2 5.11 5.11 1.02 1.02 0.52 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.89 0.89 1.1 18 0.89 1.8 1.8 0.89 1.8 1.8 1.8 1.9 0.89 0.89 0.89 1.8 7.1 35 ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0447 0.00971 0.0245 0.0125 0.0172 0.0863 3.5 3.5 3.8 4.9 8.5 3.5 3.5 3.5 5.2 0.35 0.35 0.35 0.35 0.18 0.32 4.3 0.19 0.35 0.35 0.23 0.35 0.35 0.35 0.35 0.18 0.32 0.2 0.35 1.8 12 ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1.19 5.93 5.93 5.93 5.93 5.93 5.93 5.93 5.93 5.93 5.93 5.93 5.93 5.93 1.19 5.93 5.93 5.93 5.93 11.9 11.9 5.93 5.93 1.19 1.19 0.481 0.241 0.48 2.3 2.3 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.115 0.05 0.16 0.0731 0.0966 0.0683 0.0863 0.0718 0.0834 0.0665 0.0459 0.11 0.0818 0.048 0.0487 0.0593 0.16 0.0866 0.0688 0.0456 0.114 0.0469 0.11 0.0691 0.0487 0.188 0.115 0.17 1.4 1.4 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg 5.01 5.01 5.01 5.01 5.01 5.01 5.01 5.01 5.01 5.01 5.01 5.01 5.01 1 1 5.01 5.01 5.01 5.01 10 10 5.01 5.01 1 1 18 18 18 18 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg 0.24 0.563 0.27 0.281 0.344 0.272 0.341 0.29 0.336 0.191 0.355 0.259 0.166 0.235 0.158 0.254 0.563 0.275 0.34 0.186 0.548 0.178 0.355 0.235 0.158 3.4 3.4 3.7 4.8 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3012 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3015 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S001 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3012S002 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S001 ELBS3015S002 ELBS3015S002 ELBS3015S002 ELBS3015S002 ELBS3015S002 ELBS3015S002 ELBS3015S002 ELBS3015S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:45 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 8:50 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:15 5/13/14 12:30 5/13/14 12:30 5/13/14 12:30 5/13/14 12:30 5/13/14 12:30 5/13/14 12:30 5/13/14 12:30 5/13/14 12:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0 0 0 0 0 0 0 0 0 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Analysis  Method 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 8082 Analyte Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Page 101 of 108 CAS Number 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 Result  Value 18 18 18 44 18 1.8 1.8 1.8 0.86 0.86 1 18 0.86 1.8 1.8 0.86 1.8 1.8 1.8 1.9 0.86 5.8 0.86 1.8 7 34 0.0321 0.0321 0.0473 0.0253 0.153 1.39 0.0455 0.0553 0.0491 0.0488 0.0992 0.0449 0.087 0.0951 0.0788 0.0295 0.0756 0.0278 0.434 3.17 5.71 5.71 0.434 13.4 5.71 5.71 1.14 1.14 20 20 20 20 20 20 20 6.2 20 2 2 2 0.98 0.98 1.2 20 0.98 2 2 0.98 2 2 2 2.1 0.98 0.98 0.98 2 7.9 39 22 22 22 22 22 22 22 68 22 21 21 21 21 21 21 21 21 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.044 mg/kg 0.018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00086 mg/kg 0.00086 mg/kg 0.001 mg/kg 0.018 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00086 mg/kg 0.0058 mg/kg 0.00086 mg/kg 0.0018 mg/kg 0.007 mg/kg 0.034 mg/kg 3.21E‐08 mg/kg 3.21E‐08 mg/kg 4.73E‐08 mg/kg 0.00000114 mg/kg 0.000000153 mg/kg 0.00000139 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 2.78E‐08 mg/kg 0.000000434 mg/kg 0.00000317 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.0000114 mg/kg 0.0000134 mg/kg 0.00000571 mg/kg 0.00000571 mg/kg 0.00000114 mg/kg 0.00000114 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.02 mg/kg 0.0062 mg/kg 0.02 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00098 mg/kg 0.00098 mg/kg 0.0012 mg/kg 0.02 mg/kg 0.00098 mg/kg 0.002 mg/kg 0.002 mg/kg 0.00098 mg/kg 0.002 mg/kg 0.002 mg/kg 0.002 mg/kg 0.0021 mg/kg 0.00098 mg/kg 0.00098 mg/kg 0.00098 mg/kg 0.002 mg/kg 0.0079 mg/kg 0.039 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.068 mg/kg 0.022 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg Detected N N N Y N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y N N N N N N N N N N N Y Y Y Y Y N Y Y Y Y Y N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N Project  Qual  Code Validation Note U U U U U U U U U U U U U U U U U U U U U U U U U U J J UJ UJ U UJ UJ UJ UJ UJ U UJ UJ J J J J J UJ J J J J U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U , F, F, B , F, F, B , *DVR, F, B , *DVR, F, B , F, B , *DVR, F, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, F, B , F, F, B , *DVR, F, B , *DVR, F, F, B , Original Result = 0.403 , Original Result = 0.887 , *DVR, F, F, B , F, F, B , Original Result = 0.387 , Original Result = 0.282 , Original Result = 0.183 , Original Result = 0.0898 Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.082 No 2.20E‐01 Ecological RBSL 0.043 No 4.19E‐01 Ecological RBSL 0.017 Yes 1.06E+00 MRL 0.039 Yes 1.13E+00 Ecological RBSL 0.025 No 7.20E‐01 Ecological RBSL 0.0051 No 3.53E‐01 Ecological RBSL 0.004164 No 4.32E‐01 Background 0.006101 No 2.95E‐01 Background 0.0348 No 2.47E‐02 Suburban Residential RBSL 0.073 No 1.18E‐02 Ecological RBSL 0.394 No 2.54E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.28E‐02 Ecological RBSL 0.013 No 1.38E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 3.91E‐03 Ecological RBSL 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.15E‐02 Ecological RBSL 0.087 No 6.67E‐02 Ecological RBSL 0.0017 No 5.06E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.80E‐03 Ecological RBSL 0.493 No 6.90E‐02 Suburban Residential RBSL 0.0000057 No 5.63E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 8.40E‐02 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.67E‐01 Ecological RBSL 0.18 No 1.11E‐01 Ecological RBSL 0.082 No 2.44E‐01 Ecological RBSL 0.043 No 4.65E‐01 Ecological RBSL 0.017 Yes 1.18E+00 MRL 0.039 No 1.59E‐01 Ecological RBSL 0.025 No 8.00E‐01 Ecological RBSL 0.0051 No 3.92E‐01 Ecological RBSL 0.004164 No 4.80E‐01 Background 0.006101 No 3.28E‐01 Background 0.0348 No 2.82E‐02 Suburban Residential RBSL 0.073 No 1.34E‐02 Ecological RBSL 0.394 No 3.05E‐03 Suburban Residential RBSL 1.1 No 1.82E‐02 Ecological RBSL 0.067 No 1.46E‐02 Ecological RBSL 0.013 No 1.54E‐01 Ecological RBSL 0.23 No 8.70E‐03 Ecological RBSL 0.22 No 4.45E‐03 Ecological RBSL 0.22 No 9.09E‐03 Ecological RBSL 0.0079 No 2.53E‐01 Ecological RBSL 0.0092 No 2.17E‐01 Ecological RBSL 0.0086 No 2.44E‐01 Ecological RBSL 0.075 No 1.31E‐02 Ecological RBSL 0.087 No 1.13E‐02 Ecological RBSL 0.0017 No 5.76E‐01 MRL 0.0328 No 6.10E‐02 Suburban Residential RBSL 2.5 No 3.16E‐03 Ecological RBSL 0.493 No 7.91E‐02 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.83E‐01 Ecological RBSL 0.18 No 1.22E‐01 Ecological RBSL 0.082 No 2.68E‐01 Ecological RBSL 0.043 No 5.12E‐01 Ecological RBSL 0.017 Yes 1.29E+00 MRL 0.039 Yes 1.74E+00 Ecological RBSL 0.025 No 8.80E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.75E‐01 Ecological RBSL 0.18 No 1.17E‐01 Ecological RBSL 0.082 No 2.56E‐01 Ecological RBSL 0.043 No 4.88E‐01 Ecological RBSL 0.017 Yes 1.24E+00 MRL 0.039 No 5.38E‐01 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units MDL MDL  Units 18 18 18 18 18 1.8 1.8 1.8 0.86 0.86 1 18 0.86 1.8 1.8 0.86 1.8 1.8 1.8 1.9 0.86 5.8 0.86 1.8 7 34 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 8.3 3.4 3.4 3.4 5.1 0.34 0.34 0.34 0.34 0.18 0.31 4.2 0.19 0.34 0.34 0.23 0.34 0.34 0.34 0.34 0.18 5.8 0.2 0.34 1.8 11 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 1.14 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 5.71 1.14 5.71 5.71 5.71 5.71 11.4 11.4 5.71 5.71 1.14 1.14 20 20 20 20 20 20 20 20 20 2 2 2 0.98 0.98 1.2 20 0.98 2 2 0.98 2 2 2 2.1 0.98 0.98 0.98 2 7.9 39 22 22 22 22 22 22 22 22 22 21 21 21 21 21 21 21 21 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0253 0.00571 0.0157 0.011 0.0102 0.017 0.00858 0.0171 0.0104 0.0159 0.00728 0.013 0.00919 0.00772 0.0123 0.0075 0.0157 0.00954 0.0166 0.016 0.0154 0.00749 0.013 0.0105 0.0123 3.9 3.9 4.2 5.4 9.4 3.9 3.9 3.9 5.8 0.39 0.39 0.39 0.39 0.2 0.36 4.7 0.21 0.39 0.39 0.26 0.39 0.39 0.39 0.39 0.2 0.36 0.23 0.39 2 13 4.2 4.2 4.6 5.8 10 4.2 4.2 4.2 6.2 4.2 4.2 4.5 5.8 10 4.2 4.2 4.2 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3015 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3015S002 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date 5/13/14 12:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 5.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Lab Repeat Analysis Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class PCBs Dioxin_Furans Dioxin_Furans Dioxin_Furans Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8082 1613B 1613B 1613B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 7199 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte Aroclor 1260 DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Hexavalent Chromium Aroclor 1262 Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran Page 102 of 108 CAS Number 11096825 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 117817 85687 84662 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 18540299 37324235 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 Result  Value 21 1.62 2.14 5.01 95 95 95 95 95 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 18 8.8 8.8 4.4 8.8 8.8 8.8 8.8 8.8 6.3 8.8 24.1 225 2.5 0.725 1.9 1.01 9.08 0.171 3.82 0.0973 0.75 1.68 0.0893 0.11 0.188 95.2 422 44.9 137 62.4 2180 10.3 50.8 2.66 9.9 0.56 18 18 18 18 18 18 18 9.7 18 0.35 1.8 1.8 0.88 0.88 1.1 18 0.88 1.8 1.8 0.88 1.8 1.8 1.8 1.9 0.88 0.88 0.88 1.8 7.1 35 4.88 5.02 10.6 0.676 39.1 412 3.27 0.895 3.44 1.14 18.9 0.484 8.46 0.125 1.4 2.74 0.506 Result  Value  Units ug/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.021 mg/kg 0.00000162 mg/kg 0.00000214 mg/kg 0.00000501 mg/kg 0.095 mg/kg 0.095 mg/kg 0.095 mg/kg 0.095 mg/kg 0.095 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.018 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0044 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0088 mg/kg 0.0063 mg/kg 0.0088 mg/kg 0.0000241 mg/kg 0.000225 mg/kg 0.0000025 mg/kg 0.000000725 mg/kg 0.0000019 mg/kg 0.00000101 mg/kg 0.00000908 mg/kg 0.00000506 mg/kg 0.00000382 mg/kg 0.00000506 mg/kg 0.00000506 mg/kg 0.00000168 mg/kg 0.00000506 mg/kg 0.00000101 mg/kg 0.00000101 mg/kg 0.0000952 mg/kg 0.000422 mg/kg 0.0000449 mg/kg 0.000137 mg/kg 0.0000624 mg/kg 0.00218 mg/kg 0.0000103 mg/kg 0.0000508 mg/kg 0.00000266 mg/kg 0.0000099 mg/kg 0.56 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.018 mg/kg 0.0097 mg/kg 0.018 mg/kg 0.00035 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.0011 mg/kg 0.018 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0019 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0071 mg/kg 0.035 mg/kg 0.00000488 mg/kg 0.00000502 mg/kg 0.0000106 mg/kg 0.000000676 mg/kg 0.0000391 mg/kg 0.000412 mg/kg 0.00000327 mg/kg 0.0000046 mg/kg 0.00000344 mg/kg 0.00000114 mg/kg 0.0000189 mg/kg 0.0000046 mg/kg 0.00000846 mg/kg 0.0000046 mg/kg 0.0000014 mg/kg 0.00000274 mg/kg 0.0000046 mg/kg Detected N Y Y Y N N N N N N N N N N N N N Y N N Y N N N N N Y N Y Y Y Y Y Y Y N Y N N Y N N N Y Y Y Y Y Y Y Y Y Y Y N N N N N N N Y N Y N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y N Y Y Y N Y N Y Y N Project  Qual  Code Validation Note U U U U U U U U U U U U U U UJ U J U U U U U J U J J J J J U J UJ UJ J U U UJ F, F F, F Q, Q, F Q, Q F $, F, F, B $, Q, Q, F, F, B , F, B , F, B , B , F, F , F , *DVR, F, F , *DVR, F, F , F, B F, F, B , *DVR, F $, F, F, B $, Q, Q, F, F, B J U U U U U U U J U J U U U U U U U U U U U U U U U U U U U U J J U J J U U J J U E *DVR B F, B F F, B F, B B F, B B B F, B F, B F, B F, B F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.025 No 8.40E‐01 Ecological RBSL 0.0000057 No 2.84E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 8.90E+00 Background 0.32 No 2.97E‐01 Ecological RBSL 90 No 1.06E‐03 Ecological RBSL 2.3 No 4.13E‐02 Ecological RBSL 0.11 No 8.64E‐01 Ecological RBSL 13 No 7.31E‐03 Ecological RBSL 0.0325 No 2.71E‐01 Suburban Residential RBSL 7.29 No 1.21E‐03 Suburban Residential RBSL 53 No 1.66E‐04 Ecological RBSL 1.1 No 8.00E‐03 Ecological RBSL 0.33 No 2.67E‐02 Ecological RBSL 2.2 No 4.00E‐03 Ecological RBSL 0.387 No 2.27E‐02 Suburban Residential RBSL 0.0387 No 2.27E‐01 Suburban Residential RBSL 0.387 No 4.65E‐02 Suburban Residential RBSL 7.4 No 1.19E‐03 Ecological RBSL 0.387 No 2.27E‐02 Suburban Residential RBSL 1.2 No 3.67E‐03 Ecological RBSL 0.113 No 7.79E‐02 Suburban Residential RBSL 54 No 1.63E‐04 Ecological RBSL 0.89 No 9.89E‐03 Ecological RBSL 0.387 No 2.27E‐02 Suburban Residential RBSL 14.6 No 6.03E‐04 Suburban Residential RBSL 1.3 No 4.85E‐03 Ecological RBSL 1.2 No 7.33E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 1.29 No 4.34E‐01 Suburban Residential RBSL ‐‐ No SL No SL ‐‐ No SL No SL 0.12 No 1.50E‐01 Ecological RBSL 0.18 No 1.00E‐01 Ecological RBSL 0.082 No 2.20E‐01 Ecological RBSL 0.043 No 4.19E‐01 Ecological RBSL 0.017 Yes 1.06E+00 MRL 0.039 No 2.49E‐01 Ecological RBSL 0.025 No 7.20E‐01 Ecological RBSL 0.0051 No 6.86E‐02 Ecological RBSL 0.004164 No 4.32E‐01 Background 0.006101 No 2.95E‐01 Background 0.0348 No 2.53E‐02 Suburban Residential RBSL 0.073 No 1.21E‐02 Ecological RBSL 0.394 No 2.79E‐03 Suburban Residential RBSL 1.1 No 1.64E‐02 Ecological RBSL 0.067 No 1.31E‐02 Ecological RBSL 0.013 No 1.38E‐01 Ecological RBSL 0.23 No 7.83E‐03 Ecological RBSL 0.22 No 4.00E‐03 Ecological RBSL 0.22 No 8.18E‐03 Ecological RBSL 0.0079 No 2.28E‐01 Ecological RBSL 0.0092 No 1.96E‐01 Ecological RBSL 0.0086 No 2.21E‐01 Ecological RBSL 0.075 No 1.17E‐02 Ecological RBSL 0.087 No 1.01E‐02 Ecological RBSL 0.0017 No 5.18E‐01 MRL 0.0328 No 5.49E‐02 Suburban Residential RBSL 2.5 No 2.84E‐03 Ecological RBSL 0.493 No 7.10E‐02 Suburban Residential RBSL 0.0000057 No 8.56E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 1.88E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 21 ug/kg MDL MDL  Units 6.2 ug/kg 95 95 95 95 95 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 8.8 5.06 5.06 5.06 5.06 5.06 5.06 5.06 5.06 5.06 5.06 5.06 5.06 5.06 1.01 1.01 5.06 5.06 5.06 5.06 10.1 10.1 5.06 5.06 1.01 1.01 0.42 18 18 18 18 18 18 18 18 18 1.8 1.8 1.8 0.88 0.88 1.1 18 0.88 1.8 1.8 0.88 1.8 1.8 1.8 1.9 0.88 0.88 0.88 1.8 7.1 35 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 32 32 32 32 32 3.5 3.5 3.5 3.5 1.8 1.8 3.5 3.5 3.5 3.5 3.5 1.8 3.5 3.5 3.5 3.5 3.5 3.5 3.5 0.0963 0.233 0.155 0.16 0.257 0.152 0.269 0.171 0.258 0.0941 0.325 0.159 0.0893 0.11 0.185 0.119 0.233 0.16 0.261 0.121 0.207 0.0916 0.325 0.11 0.185 0.15 3.5 3.5 3.8 4.8 8.4 3.5 3.5 3.5 5.1 0.35 0.35 0.35 0.35 0.18 0.32 4.2 0.19 0.35 0.35 0.23 0.35 0.35 0.35 0.35 0.18 0.32 0.2 0.35 1.8 12 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.921 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 4.6 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.186 0.193 0.759 0.307 0.191 0.298 0.19 0.311 0.293 0.324 0.124 0.245 0.195 0.126 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N Y Y N Y Y Y Y Y Y Y N N Y N Y Y Y N Y N Y Y N N N N Y N N N Y N N N N Y N N N N N N N N N N N N Y N N N N N N N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y N Y Y Y Y N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3016 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3017 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3016S001SP ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3017S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 ELBS3016S001 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/14/14 10:30 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 8:15 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 7196A 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8082 8082 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 2,3,7,8‐TCDD Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Hexavalent Chromium bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1268 Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 Aroclor 1262 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan I Endosulfan II Endosulfan sulfate Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Methoxychlor Mirex Toxaphene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran Page 103 of 108 CAS Number 1746016 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 18540299 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 11100144 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 72548 72559 50293 309002 319846 319857 57749 319868 60571 959988 33213659 1031078 72208 7421934 53494705 58899 76448 1024573 72435 2385855 8001352 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 Result  Value 0.372 78 3640 815 176 311 75.6 175 16.1 27.7 3.88 0.131 18.3 18.3 18.3 18.3 35.7 18.3 18.3 3.45 3.45 3.45 3.45 3.45 2.94 1.21 1.9 1.55 3.45 1.04 3.45 2.25 3.45 1.04 3.45 2.07 2.25 3.66 3.66 3.66 3.66 3.66 3.66 2.52 2.08 3.66 7.31 7.31 7.31 3.66 3.66 3.66 45.7 3.66 7.31 3.66 7.31 7.31 7.31 7.31 7.31 3.66 3.66 3.66 36.6 3.66 91.4 0.66 0.338 0.424 0.213 2.1 10.1 0.166 0.187 0.158 0.102 0.488 0.155 0.461 0.974 0.102 0.127 0.201 0.0288 5.78 20.2 2.78 3.31 8.31 105 3.19 4.58 2.61 1.26 0.512 0.685 1.27 4.53 44.1 0.282 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.000000921 mg/kg 0.000078 mg/kg 0.00364 mg/kg 0.000815 mg/kg 0.000176 mg/kg 0.000311 mg/kg 0.0000756 mg/kg 0.000175 mg/kg 0.0000161 mg/kg 0.0000277 mg/kg 0.00000388 mg/kg 0.437 mg/kg 0.0183 mg/kg 0.0183 mg/kg 0.0183 mg/kg 0.0183 mg/kg 0.0183 mg/kg 0.0183 mg/kg 0.0183 mg/kg 0.00345 mg/kg 0.00345 mg/kg 0.00345 mg/kg 0.00345 mg/kg 0.00345 mg/kg 0.00294 mg/kg 0.00121 mg/kg 0.0019 mg/kg 0.00155 mg/kg 0.00345 mg/kg 0.00104 mg/kg 0.00345 mg/kg 0.00225 mg/kg 0.00345 mg/kg 0.00104 mg/kg 0.00345 mg/kg 0.00207 mg/kg 0.00225 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00252 mg/kg 0.00208 mg/kg 0.00366 mg/kg 0.00731 mg/kg 0.00731 mg/kg 0.00731 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.0457 mg/kg 0.00366 mg/kg 0.00731 mg/kg 0.00366 mg/kg 0.00731 mg/kg 0.00731 mg/kg 0.00731 mg/kg 0.00731 mg/kg 0.00731 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.0366 mg/kg 0.00366 mg/kg 0.0914 mg/kg 0.00000066 mg/kg 0.000000338 mg/kg 0.000000424 mg/kg 0.000000213 mg/kg 0.0000021 mg/kg 0.0000101 mg/kg 0.0000063 mg/kg 0.000000187 mg/kg 0.000000158 mg/kg 0.0000063 mg/kg 0.000000488 mg/kg 0.000000155 mg/kg 0.000000461 mg/kg 0.000000974 mg/kg 0.0000063 mg/kg 0.000000127 mg/kg 0.000000201 mg/kg 0.00000126 mg/kg 0.00000578 mg/kg 0.0000202 mg/kg 0.00000278 mg/kg 0.00000331 mg/kg 0.00000831 mg/kg 0.000105 mg/kg 0.00000319 mg/kg 0.00000458 mg/kg 0.00000261 mg/kg 0.00000126 mg/kg 0.000000512 mg/kg 0.000000685 mg/kg 0.00000127 mg/kg 0.00000453 mg/kg 0.0000441 mg/kg 0.00000509 mg/kg Detected N Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N Y Y Y Y N Y N Y N Y N Y Y N N N N N N Y Y N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y N Y Y N Y Y Y Y N Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Project  Qual  Code U U U UJ UJ UJ U UJ UJ UJ UJ UJ UJ UJ J J J J UJ J UJ J UJ J UJ J J U U U U U U J J U U U U U U U U U U U U U U U U U U U U U U J J U J J U J J J J UJ J J UJ J J J J Validation Note F, B F F, B H, F, Original Result = 7.14 H H H H, F, B F, H H L L L L L L L L L L L L L L L F, L L L *DVR , F, F, B , F, F, B , F, B , F, B , F, B , F, F, B , B , F, B , F, B , F, F, B , *DVR, F, F, B , F, B , F, F, B , *DVR , F, F, B , F, F, B J J J , Original Result = 0.226 J , F, F, B , F, F, B , *DVR, F, B UJ Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 1.29 No 3.39E‐01 Suburban Residential RBSL 0.32 No 5.72E‐02 Ecological RBSL 90 No 2.03E‐04 Ecological RBSL 2.3 No 7.96E‐03 Ecological RBSL 4.5 No 4.07E‐03 Ecological RBSL 0.11 No 1.66E‐01 Ecological RBSL 13 No 1.41E‐03 Ecological RBSL 0.0325 No 5.63E‐01 Suburban Residential RBSL 7.29 No 4.73E‐04 Suburban Residential RBSL 53 No 6.51E‐05 Ecological RBSL 1.1 No 3.14E‐03 Ecological RBSL 0.33 No 1.05E‐02 Ecological RBSL 2.2 No 1.57E‐03 Ecological RBSL 0.387 No 7.60E‐03 Suburban Residential RBSL 0.0387 No 3.13E‐02 Suburban Residential RBSL 0.387 No 4.91E‐03 Suburban Residential RBSL 7.4 No 2.09E‐04 Ecological RBSL 0.387 No 8.91E‐03 Suburban Residential RBSL 1.2 No 8.67E‐04 Ecological RBSL 0.113 No 3.05E‐02 Suburban Residential RBSL 54 No 4.17E‐05 Ecological RBSL 0.89 No 3.88E‐03 Ecological RBSL 0.387 No 2.69E‐03 Suburban Residential RBSL 14.6 No 2.36E‐04 Suburban Residential RBSL 1.3 No 1.59E‐03 Ecological RBSL 1.2 No 1.88E‐03 Ecological RBSL ‐‐ No SL No SL 0.12 No 3.05E‐02 Ecological RBSL 0.18 No 2.03E‐02 Ecological RBSL 0.082 No 4.46E‐02 Ecological RBSL 0.043 No 8.51E‐02 Ecological RBSL 0.017 No 2.15E‐01 MRL 0.039 No 6.46E‐02 Ecological RBSL 0.025 No 8.32E‐02 Ecological RBSL ‐‐ No SL No SL 0.0051 Yes 1.43E+00 Ecological RBSL 0.004164 Yes 1.76E+00 Background 0.006101 Yes 1.20E+00 Background 0.0348 No 1.05E‐01 Suburban Residential RBSL 0.073 No 5.01E‐02 Ecological RBSL 0.394 No 9.29E‐03 Suburban Residential RBSL 1.1 No 4.15E‐02 Ecological RBSL 0.067 No 5.46E‐02 Ecological RBSL 0.013 No 5.62E‐01 Ecological RBSL 0.22 No 1.66E‐02 Ecological RBSL 0.22 No 3.32E‐02 Ecological RBSL 0.23 No 3.18E‐02 Ecological RBSL 0.0079 No 9.25E‐01 Ecological RBSL 0.0092 No 7.95E‐01 Ecological RBSL 0.0086 No 8.50E‐01 Ecological RBSL 0.075 No 4.88E‐02 Ecological RBSL 0.087 No 4.21E‐02 Ecological RBSL 0.0017 Yes 2.15E+00 MRL 2.5 No 1.46E‐02 Ecological RBSL 0.0328 No 1.12E‐01 Suburban Residential RBSL 0.493 No 1.85E‐01 Suburban Residential RBSL 0.0000057 No 1.16E‐01 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 7.53E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.0000057 No 8.98E‐02 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 2.26E+00 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 0.921 9.21 9.21 4.6 4.6 4.6 4.6 4.6 4.6 0.921 0.921 0.437 18.3 18.3 18.3 18.3 18.3 18.3 18.3 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.45 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 7.31 7.31 7.31 3.66 3.66 3.66 45.7 3.66 7.31 3.66 7.31 7.31 7.31 7.31 7.31 3.66 3.66 3.66 36.6 3.66 91.4 1.26 6.3 6.3 6.3 6.3 6.3 6.3 6.3 6.3 6.3 6.3 6.3 6.3 6.3 1.26 6.3 6.3 6.3 6.3 12.6 12.6 6.3 6.3 1.26 1.26 RL Units MDL ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.124 0.309 0.812 0.759 0.193 0.298 0.19 0.245 0.0285 0.124 0.13 0.131 5.49 5.49 5.49 5.49 5.49 5.49 5.49 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.864 0.518 0.864 0.864 1.22 1.22 1.22 1.22 1.22 1.22 1.22 1.22 1.22 1.83 1.83 1.83 0.914 0.914 0.914 9.14 0.914 1.83 0.914 1.83 1.83 1.83 1.83 1.83 0.914 0.914 0.914 9.14 0.914 30.4 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 5.09 ng/kg 5.09 ng/kg 5.09 ng/kg 0.0333 0.0121 0.029 0.0182 0.0292 0.0321 0.0244 0.0326 0.0304 0.0317 0.016 0.0312 0.0259 0.0146 0.0219 0.0145 0.029 0.0273 0.0321 0.0179 0.0283 0.0152 0.0312 0.0288 0.0219 MDL  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0108 ng/kg 0.0421 ng/kg 0.0193 ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N Y Y N N N N N N N Y Y N Y N N N Y N Y N N Y Y Y Y Y Y Y N Y Y N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3020 ELBS3021 ELBS3021 ELBS3021 ELBS3022 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3023 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S001 ELBS3020S002 ELBS3021D001 ELBS3021S001 ELBS3021S002 ELBS3022S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3023S001SP ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3021S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 ELBS3023S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:40 5/13/14 9:55 6/17/14 10:15 6/17/14 10:15 6/17/14 10:30 6/17/14 11:30 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 12:45 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 1 1 3 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 3.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Confirmation Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Lab Repeat Analysis Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Metals Metals Metals Metals Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 6010B 6020 7199 7199 7199 7199 7199 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B Analyte 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Sodium Arsenic Hexavalent Chromium Hexavalent Chromium Hexavalent Chromium Hexavalent Chromium Hexavalent Chromium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 2,3,7,8‐Tetrachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran Page 104 of 108 CAS Number 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 7440235 7440382 18540299 18540299 18540299 18540299 18540299 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 51207319 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 39001020 3268879 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 Result  Value 0.235 0.72 0.223 1.67 0.224 1.68 0.103 0.435 0.328 0.0599 0.0146 0.0717 9.68 106 6.09 14.8 10.9 848 1.55 2.43 0.522 0.399 102 9.09 0.78 0.67 0.88 0.5 0.65 18.6 20.9 39 0.694 181 1380 15.7 6.1 12.3 5.95 59.5 0.109 26.8 2.69 6.01 10.2 2.6 0.714 703 3010 322 791 394 13900 63.4 415 16.7 107 20.9 21.6 40.3 1.24 157 1420 13.5 5.34 11.7 4.72 61.7 1.84 29.9 0.746 6.64 9.37 1.57 0.709 349 13100 3020 719 1030 273 494 61.7 136 13.3 7.55 7.87 18.2 89.6 809 7.91 2.42 6.25 2.73 33.4 1.11 15 1.5 3.41 4.59 1.15 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Result  in SL Units SL Units 0.00000509 mg/kg 0.00000072 mg/kg 0.000000223 mg/kg 0.00000167 mg/kg 0.000000224 mg/kg 0.00000168 mg/kg 0.00000509 mg/kg 0.00000509 mg/kg 0.00000509 mg/kg 0.00000509 mg/kg 0.00000102 mg/kg 7.17E‐08 mg/kg 0.00000968 mg/kg 0.000106 mg/kg 0.00000609 mg/kg 0.0000148 mg/kg 0.0000109 mg/kg 0.000848 mg/kg 0.00000155 mg/kg 0.00000243 mg/kg 0.000000522 mg/kg 0.000000399 mg/kg 102 mg/kg 9.09 mg/kg 0.78 mg/kg 0.67 mg/kg 0.88 mg/kg 0.5 mg/kg 0.65 mg/kg 0.0000186 mg/kg 0.0000209 mg/kg 0.000039 mg/kg 0.000000694 mg/kg 0.000181 mg/kg 0.00138 mg/kg 0.0000157 mg/kg 0.0000061 mg/kg 0.0000123 mg/kg 0.00000595 mg/kg 0.0000595 mg/kg 0.00000522 mg/kg 0.0000268 mg/kg 0.00000269 mg/kg 0.00000601 mg/kg 0.0000102 mg/kg 0.00000522 mg/kg 0.000000714 mg/kg 0.000703 mg/kg 0.00301 mg/kg 0.000322 mg/kg 0.000791 mg/kg 0.000394 mg/kg 0.0139 mg/kg 0.0000634 mg/kg 0.000415 mg/kg 0.0000167 mg/kg 0.000107 mg/kg 0.0000209 mg/kg 0.0000216 mg/kg 0.0000403 mg/kg 0.00000124 mg/kg 0.000157 mg/kg 0.00142 mg/kg 0.0000135 mg/kg 0.00000534 mg/kg 0.0000117 mg/kg 0.00000472 mg/kg 0.0000617 mg/kg 0.00000184 mg/kg 0.0000299 mg/kg 0.00000499 mg/kg 0.00000664 mg/kg 0.00000937 mg/kg 0.00000157 mg/kg 0.000000709 mg/kg 0.000349 mg/kg 0.0131 mg/kg 0.00302 mg/kg 0.000719 mg/kg 0.00103 mg/kg 0.000273 mg/kg 0.000494 mg/kg 0.0000617 mg/kg 0.000136 mg/kg 0.0000133 mg/kg 0.00000755 mg/kg 0.00000787 mg/kg 0.0000182 mg/kg 0.0000896 mg/kg 0.000809 mg/kg 0.00000791 mg/kg 0.00000242 mg/kg 0.00000625 mg/kg 0.00000273 mg/kg 0.0000334 mg/kg 0.00000111 mg/kg 0.000015 mg/kg 0.0000015 mg/kg 0.00000502 mg/kg 0.00000459 mg/kg 0.00000115 mg/kg Detected N Y Y Y Y Y N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Project  Qual  Code UJ J J J J J U UJ UJ UJ U J Validation Note , *DVR, F, B , F, B , F, F, B , F, B , F, B , F, B , F, F, B , *DVR, F, F, B , *DVR, F, B , *DVR, F, F, B , F, F, B , F, F, B J J J J J Q, Q J , F, B , F, B , F, B , F, B U J UJ J J J J UJ J J J J J J J J UJ J J , B , B , F , B , F, B , F, B , F, B , *DVR, F, B , B , F, B , F, B , F, B , F, B , F, B C, F, B , F, B , F, B , F, B , F, B F, B Q, Q, F, B F, B F, B B B B F, B B *DVR, F, B F, B F, B F, B F, B Q, Q, C, F, B F, B F, B F, B , F, B F, B , F, B , F , F , F, B , F, B , F, B , F, B , B , B , F , B , F, B , *DVR, F, B , F, B , F, B Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL 754 No 1.35E‐01 Background 24.2 No 3.76E‐01 Background 1.29 No 6.05E‐01 Suburban Residential RBSL 1.29 No 5.19E‐01 Suburban Residential RBSL 1.29 No 6.82E‐01 Suburban Residential RBSL 1.29 No 3.88E‐01 Suburban Residential RBSL 1.29 No 5.04E‐01 Suburban Residential RBSL 0.0000057 Yes 3.26E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 6.93E+01 Background ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.0000057 Yes 3.67E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 7.16E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.0000057 Yes 1.32E+00 Ecological RBSL ‐‐ No SL No SL 0.000000563 Yes 3.23E+01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 5.09 5.09 5.09 5.09 5.09 5.09 5.09 5.09 5.09 5.09 1.02 1.02 5.09 5.09 5.09 5.09 10.2 10.2 5.09 5.09 1.02 1.02 50.6 0.405 0.53 0.43 0.45 0.45 0.44 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 0.0263 0.0313 0.0225 0.0316 0.026 0.0313 0.0112 0.031 0.0251 0.0114 0.0146 0.0225 0.0138 0.0421 0.0249 0.0314 0.0177 0.0397 0.0113 0.031 0.0146 0.0225 16.9 0.158 0.19 0.15 0.16 0.16 0.16 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 1.04 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 5.22 1.04 5.22 5.22 5.22 5.22 10.4 10.4 5.22 5.22 1.04 1.04 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0966 0.0749 0.251 0.109 0.104 0.11 0.103 0.115 0.109 0.106 0.0498 0.181 0.102 0.0508 0.135 0.0888 0.251 0.104 0.11 0.0727 0.216 0.0503 0.181 0.104 0.135 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.998 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 4.99 0.998 9.98 9.98 4.99 4.99 4.99 4.99 4.99 4.99 0.998 0.998 5.02 5.02 5.02 5.02 5.02 5.02 5.02 5.02 5.02 5.02 5.02 5.02 5.02 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.377 0.449 1.52 0.721 0.421 0.699 0.417 0.681 0.575 0.731 0.411 0.317 0.457 0.369 0.299 0.415 1.69 1.52 0.449 0.681 0.417 0.317 0.0647 0.299 0.399 0.0684 0.247 0.1 0.0768 0.101 0.07 0.105 0.0817 0.103 0.0532 0.167 0.074 0.05 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y N N N N Y N Y Y Y Y N N N Y N Y N Y N N Y N Y Y Y N Y N Y Y Y Y N Y N N N N Y Y Y N Y N Y N N N Y Y Y N Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 ELBS3024 GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012A GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S001 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 ELBS3024S002 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012AS001SP GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012AS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Collection  Date 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:15 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 6/17/14 13:30 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:00 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.7 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 3.5 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Calculated Result Calculated Result Calculated Result Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result HZ Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Analysis  Method 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM Analyte 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐Tetrachlorodibenzofuran 2,3,7,8‐TCDD Heptachlorodibenzofurans Heptachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Pentachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Page 105 of 108 CAS Number 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 51207319 1746016 38998753 37871004 55684941 34465468 39001020 3268879 30402154 36088229 55722275 41903575 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 90120 91576 83329 208968 120127 56553 50328 Result  Value 0.524 0.259 348 1540 134 291 262 6850 31.5 124 10.6 34.6 0.0543 0.139 0.221 1.71 14.6 0.283 0.104 0.188 0.119 0.693 0.105 0.322 0.0552 0.0712 0.174 0.0346 0.0711 0.08 5.88 28.9 3.22 6.38 4.92 127 1.03 1.94 0.634 1.02 1.2 1.5 1.8 1.8 1.8 1.8 1.8 0.88 1.8 1.8 1.2 1.8 1.8 1.8 1.8 1.7 1.2 1.8 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 0.914 3.66 9.3 9.3 9.3 9.3 9.3 3.9 4.3 6.3 9.3 4.1 5.7 9.3 9.3 9.3 9.3 9.3 9.3 9.3 3.89 3.89 3.89 3.89 3.89 3.89 3.89 Result  Value  Units ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Result  in SL Units SL Units 0.000000524 mg/kg 0.000001 mg/kg 0.000348 mg/kg 0.00154 mg/kg 0.000134 mg/kg 0.000291 mg/kg 0.000262 mg/kg 0.00685 mg/kg 0.0000315 mg/kg 0.000124 mg/kg 0.0000106 mg/kg 0.0000346 mg/kg 5.43E‐08 mg/kg 0.000000139 mg/kg 0.000000221 mg/kg 0.00000171 mg/kg 0.0000146 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.000000188 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000503 mg/kg 0.00000101 mg/kg 0.00000101 mg/kg 0.00000588 mg/kg 0.0000289 mg/kg 0.00000322 mg/kg 0.00000638 mg/kg 0.00000492 mg/kg 0.000127 mg/kg 0.00000103 mg/kg 0.00000194 mg/kg 0.000000634 mg/kg 0.00000102 mg/kg 0.0012 mg/kg 0.0015 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.00088 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0012 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0018 mg/kg 0.0017 mg/kg 0.0012 mg/kg 0.0018 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.00366 mg/kg 0.000914 mg/kg 0.00366 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0039 mg/kg 0.0043 mg/kg 0.0063 mg/kg 0.0093 mg/kg 0.0041 mg/kg 0.0057 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.0093 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg Detected Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N Y N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y N N N N N Y N N Y N N N N Y Y N N N N N N N N N N N N N N N N N Y N N N N N N Y Y Y N Y Y N N N N N N N N N N N N N N Project  Qual  Code J UJ J J UJ UJ J UJ UJ UJ UJ UJ UJ UJ UJ U UJ J J J J J J J UJ UJ UJ UJ UJ J UJ UJ J UJ UJ UJ UJ J J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ J UJ UJ UJ UJ UJ UJ J J J UJ J J UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ UJ Validation Note , *DVR, B , F, B , F, B , F, B , F, B , F, B C, F, B , F, B , F, B , F, B , F, B , F, B , F, B , *DVR, F, B , *DVR, F, B , *DVR, B , *DVR, B , *DVR, F , *DVR, B , *DVR, F, B , *DVR, F, B , *DVR, F, B , *DVR, F, B , *DVR, B , F, B , F, B , F, B , F, B , F, B , F, B , F, B , F, B , F, B , F, B H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H H Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.0000057 No 9.53E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 3.93E‐01 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 7.29 No 1.65E‐04 Suburban Residential RBSL 53 No 2.83E‐05 Ecological RBSL 1.1 No 1.64E‐03 Ecological RBSL 0.33 No 5.45E‐03 Ecological RBSL 2.2 No 8.18E‐04 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 0.0387 No 4.65E‐02 Suburban Residential RBSL 0.387 No 2.27E‐03 Suburban Residential RBSL 7.4 No 2.43E‐04 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 1.2 No 1.00E‐03 Ecological RBSL 0.113 No 1.59E‐02 Suburban Residential RBSL 54 No 3.33E‐05 Ecological RBSL 0.89 No 2.02E‐03 Ecological RBSL 0.387 No 4.65E‐03 Suburban Residential RBSL 14.6 No 1.16E‐04 Suburban Residential RBSL 1.3 No 9.23E‐04 Ecological RBSL 1.2 No 1.50E‐03 Ecological RBSL 7.29 No 5.02E‐04 Suburban Residential RBSL 53 No 6.91E‐05 Ecological RBSL 1.1 No 3.33E‐03 Ecological RBSL 0.33 No 1.11E‐02 Ecological RBSL 2.2 No 1.66E‐03 Ecological RBSL 0.387 No 9.46E‐03 Suburban Residential RBSL 0.0387 No 9.46E‐02 Suburban Residential RBSL 0.387 No 9.46E‐03 Suburban Residential RBSL 7.4 No 4.95E‐04 Ecological RBSL 0.387 No 9.46E‐03 Suburban Residential RBSL 1.2 No 3.05E‐03 Ecological RBSL 0.113 No 3.24E‐02 Suburban Residential RBSL 54 No 6.78E‐05 Ecological RBSL 0.89 No 4.11E‐03 Ecological RBSL 0.387 No 9.46E‐03 Suburban Residential RBSL 14.6 No 2.51E‐04 Suburban Residential RBSL 1.3 No 7.03E‐04 Ecological RBSL 1.2 No 3.05E‐03 Ecological RBSL 7.29 No 1.28E‐03 Suburban Residential RBSL 53 No 1.75E‐04 Ecological RBSL 1.1 No 8.45E‐03 Ecological RBSL 0.33 No 2.82E‐02 Ecological RBSL 2.2 No 4.23E‐03 Ecological RBSL 0.387 No 1.01E‐02 Suburban Residential RBSL 0.0387 No 1.11E‐01 Suburban Residential RBSL 0.387 No 1.63E‐02 Suburban Residential RBSL 7.4 No 1.26E‐03 Ecological RBSL 0.387 No 1.06E‐02 Suburban Residential RBSL 1.2 No 4.75E‐03 Ecological RBSL 0.113 No 8.23E‐02 Suburban Residential RBSL 54 No 1.72E‐04 Ecological RBSL 0.89 No 1.04E‐02 Ecological RBSL 0.387 No 2.40E‐02 Suburban Residential RBSL 14.6 No 6.37E‐04 Suburban Residential RBSL 1.3 No 7.15E‐03 Ecological RBSL 1.2 No 7.75E‐03 Ecological RBSL 7.29 No 5.34E‐04 Suburban Residential RBSL 53 No 7.34E‐05 Ecological RBSL 1.1 No 3.54E‐03 Ecological RBSL 0.33 No 1.18E‐02 Ecological RBSL 2.2 No 1.77E‐03 Ecological RBSL 0.387 No 1.01E‐02 Suburban Residential RBSL 0.0387 No 1.01E‐01 Suburban Residential RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL MDL  Units RL Units MDL 1 1 5.02 5.02 5.02 5.02 10 10 5.02 5.02 1 1 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 0.0913 0.106 0.0812 0.247 0.0754 0.103 0.0787 0.163 0.0516 0.167 0.0913 0.106 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg 5.03 5.03 5.03 5.03 5.03 5.03 5.03 5.03 5.03 5.03 5.03 5.03 5.03 1.01 1.01 5.03 5.03 5.03 5.03 10.1 10.1 5.03 5.03 1.01 1.01 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 1.8 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 3.66 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 3.89 3.89 3.89 3.89 3.89 3.89 3.89 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0283 0.0628 0.0539 0.053 0.0541 0.0447 0.057 0.0638 0.0571 0.0272 0.0575 0.0484 0.0291 0.0711 0.0757 0.0371 0.0628 0.0516 0.056 0.0764 0.064 0.0281 0.0575 0.0711 0.0757 0.74 0.74 0.74 0.37 0.37 0.74 0.74 0.74 0.74 0.74 0.37 0.74 0.74 0.74 0.74 0.74 0.74 0.74 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.914 0.548 0.914 0.914 3.7 3.7 3.7 1.9 1.9 3.7 3.7 3.7 3.7 3.7 1.9 3.7 3.7 3.7 3.7 3.7 3.7 3.7 0.973 0.973 0.973 0.973 0.973 0.973 0.973 ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ng/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y N N N N N N N Y Y Y Y Y N N Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B GMBS2012B MH02072993 STBS3008 STBS3008 STBS3008 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP GMBS2012BS001SP 072993MH02 STBS3008S001 STBS3008S002 STBS3008S002SP SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 GMBS2012BS001 STBS3008S002 Sample ID Sample Type Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample 072993MH02 Primary Sample Primary Sample Primary Sample Split Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 1/27/14 12:45 7/29/93 0:00 5/15/14 8:45 5/15/14 9:00 5/15/14 9:00 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.6 Sample  Bottom  Depth (feet bgs) 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 1.1 0 5 5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 0.5 6 6 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 Sample Top  Depth (feet bgs) Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result HZ Primary Result HZ Primary Result Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Hydrocarbons Metals Metals Metals Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 418.1 6020 6020 6020 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8015B 8015B 8015B 8015B 314.0‐DI WET 9045C 9056 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7196A 7471A 8270C SIM 8270C SIM Analyte Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Hydrocarbons Cadmium Cadmium Cadmium DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Perchlorate pH Bromide Chloride Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Antimony Beryllium Boron Lithium Potassium Sodium Zinc Zirconium Arsenic Barium Cadmium Chromium Cobalt Copper Lead Molybdenum Nickel Selenium Silver Thallium Vanadium Hexavalent Chromium Mercury bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Page 106 of 108 CAS Number 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 8012951 7440439 7440439 7440439 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 35822469 67562394 55673897 39227286 70648269 57653857 57117449 19408743 72918219 40321764 57117416 60851345 57117314 1746016 51207319 3268879 39001020 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 14797730 E‐10139 24959679 16887006 16984488 NO3N NO2 14265442 14808798 7429905 7440360 7440417 7440428 7439932 7440097 7440235 7440666 7440677 7440382 7440393 7440439 7440473 7440484 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7440622 18540299 7439976 117817 85687 Result  Value 3.89 0.973 3.89 3.89 3.89 3.89 3.89 3.89 3.89 1.36 1.56 120 0.215 0.109 0.106 0.0275 0.0275 0.0467 0.271 0.125 0.186 0.128 0.0994 0.186 0.0963 0.132 0.254 0.0875 0.0822 0.102 0.0885 0.0752 0.0982 8.51 0.325 0.543 0.153 0.186 0.39 0.0875 0.0853 0.0752 0.157 240 240 1000 240 1000 240 240 240 240 240 380 240 240 4800 3800 240 240 480 5.6 5.6 5.6 2.2 4.5 7.7 0.44 13 5 2 0.38 0.56 39 16000 0.43 1.2 5.6 21 1700 200 41 2.4 7 92 0.21 24 7.7 12 6.6 0.14 17 0.76 0.063 0.27 45 0.04 0.0094 22 22 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Result  in SL Units SL Units 0.00389 mg/kg 0.000973 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00389 mg/kg 0.00136 mg/kg 0.00156 mg/kg 120 mg/kg 0.215 mg/kg 0.109 mg/kg 0.106 mg/kg 2.75E‐08 mg/kg 2.75E‐08 mg/kg 4.67E‐08 mg/kg 0.000000271 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.000000186 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.000000254 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.000000851 mg/kg 0.000000851 mg/kg 0.00000851 mg/kg 0.00000851 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.000000186 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.00000426 mg/kg 0.000000851 mg/kg 0.000000157 mg/kg 0.24 mg/kg 0.24 mg/kg 1 mg/kg 0.24 mg/kg 1 mg/kg 0.24 mg/kg 0.24 mg/kg 0.24 mg/kg 0.24 mg/kg 0.24 mg/kg 0.38 mg/kg 0.24 mg/kg 0.24 mg/kg 4.8 mg/kg 3.8 mg/kg 0.24 mg/kg 0.24 mg/kg 0.48 mg/kg 5.6 mg/kg 5.6 mg/kg 5.6 mg/kg 2.2 mg/kg 0.0045 mg/kg 7.7 ph Units 5.6 mg/kg 13 mg/kg 5 mg/kg 2 mg/kg 5.6 mg/kg 5.6 mg/kg 39 mg/kg 16000 mg/kg 1.1 mg/kg 1.2 mg/kg 5.6 mg/kg 21 mg/kg 1700 mg/kg 200 mg/kg 41 mg/kg 2.4 mg/kg 7 mg/kg 92 mg/kg 0.21 mg/kg 24 mg/kg 7.7 mg/kg 12 mg/kg 6.6 mg/kg 0.14 mg/kg 17 mg/kg 0.76 mg/kg 0.063 mg/kg 0.27 mg/kg 45 mg/kg 0.11 mg/kg 0.0094 mg/kg 0.022 mg/kg 0.022 mg/kg Detected N Y N N N N N N N Y Y Y Y Y Y Y Y Y Y N N N N Y N N Y N N N N N N N N N N Y N N N N Y N N N N N N N N N N N N N N N N N N N N N Y N Y N Y Y Y N N Y Y N Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N Project  Qual  Code UJ J UJ UJ UJ UJ UJ UJ UJ J J Validation Note H H H H H H H H H H H J J U U U U J U U J U U U U U U U U U U J U U U U J U U UJ U UJ U U U U U U U U U U U U U U U U J U J U B F, Original Result = 2.06 B B B B Q, Q, L Q, Q Q Q Q L, L J J U U UJ U Q, Q Q, Q , F, Original Result = 1.4 B J J $, , , , B $, B J J B U J U U F, F F, F, B, Original Result = 7.1 F, F, Original Result = 0.34 Ratio Boeing Exceeds Boeing Soil Char Boeing SCL Basis Soil Char Soil Char Level Level Level  (mg/kg) 0.387 No 1.01E‐02 Suburban Residential RBSL 7.4 No 1.31E‐04 Ecological RBSL 0.387 No 1.01E‐02 Suburban Residential RBSL 1.2 No 3.24E‐03 Ecological RBSL 0.113 No 3.44E‐02 Suburban Residential RBSL 54 No 7.20E‐05 Ecological RBSL 0.89 No 4.37E‐03 Ecological RBSL 0.387 No 1.01E‐02 Suburban Residential RBSL 14.6 No 2.66E‐04 Suburban Residential RBSL 1.3 No 1.05E‐03 Ecological RBSL 1.2 No 1.30E‐03 Ecological RBSL ‐‐ No SL No SL 0.435 No 4.94E‐01 Background 0.435 No 2.51E‐01 Background 0.435 No 2.44E‐01 Background 0.0000057 No 4.82E‐03 Ecological RBSL ‐‐ No SL No SL 0.000000563 No 8.29E‐02 Background ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL No SL No SL ‐‐ ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 0.92 No 2.61E‐01 Ecological RBSL 0.3 No 8.00E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL 0.3 No 8.00E‐01 MRL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 110 No 2.18E‐03 Ecological RBSL ‐‐ No SL No SL No SL ‐‐ No SL ‐‐ No SL No SL 0.3 No 8.00E‐01 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL 1400 No 4.00E‐03 1400 No 4.00E‐03 1400 No 4.00E‐03 1 Yes 2.20E+00 0.5 No 9.00E‐03 Ecological RBSL ‐‐ No SL No SL ‐‐ No SL No SL ‐‐ No SL No SL 35 No 1.43E‐01 Ecological RBSL 2340 No 8.55E‐04 Ecological RBSL ‐‐ No SL No SL 863.2 No 6.49E‐03 Background ‐‐ No SL No SL 37900 No 4.22E‐01 Background 0.5 Yes 2.20E+00 MRL 4.8 No 2.50E‐01 Ecological RBSL 22 No 2.55E‐01 Ecological RBSL 64.4 No 3.26E‐01 Background 7524 No 2.26E‐01 Background 754 No 2.65E‐01 Background 153 No 2.68E‐01 Background 10.64 No 2.26E‐01 Background 24.2 No 2.89E‐01 Background 203.8 No 4.51E‐01 Background 0.435 No 4.83E‐01 Background 60.11 No 3.99E‐01 Background 26.18 No 2.94E‐01 Background 42 No 2.86E‐01 Background 33.9 No 1.95E‐01 Background 1.642 No 8.53E‐02 Background 64.2 No 2.65E‐01 Background 1 No 7.60E‐01 MRL 0.99 No 6.36E‐02 Ecological RBSL 0.761 No 3.55E‐01 Suburban Residential RBSL 111.8 No 4.03E‐01 Background 1.29 No 8.53E‐02 Suburban Residential RBSL 0.87 No 1.08E‐02 Ecological RBSL 0.32 No 6.88E‐02 Ecological RBSL 90 No 2.44E‐04 Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 3.89 3.89 3.89 3.89 3.89 3.89 3.89 3.89 3.89 3.89 3.89 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.1 mg/kg 0.106 mg/kg 0.186 mg/kg 4.26 4.26 4.26 4.26 4.26 4.26 4.26 4.26 4.26 4.26 4.26 4.26 4.26 0.851 0.851 8.51 8.51 4.26 4.26 4.26 4.26 4.26 4.26 0.851 0.851 240 240 1000 240 1000 240 240 240 240 240 380 240 240 4800 3800 240 240 480 5.6 5.6 5.6 5.6 4.5 0.1 5.6 5.6 5.6 5.6 5.6 5.6 5.6 11 1.1 0.56 5.6 7.1 110 130 5.6 28 0.56 0.56 0.22 1.1 0.56 0.22 0.45 0.11 0.45 1.1 0.22 0.22 1.1 0.11 0.034 22 22 pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg MDL 0.973 0.973 0.973 0.973 0.973 0.973 0.973 0.973 0.584 0.973 0.973 MDL  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg 0.0461 mg/kg 0.049 mg/kg 0.0186 mg/kg 0.173 0.125 0.186 0.128 0.0994 0.125 0.0963 0.132 0.13 0.0875 0.0822 0.102 0.0885 0.0752 0.0982 0.261 0.229 0.173 0.153 0.129 0.106 0.0875 0.0853 0.0752 0.0982 59 55 100 48 180 52 44 81 53 38 100 74 59 1600 1300 82 68 53 1.1 1.1 1.1 1.1 0.31 pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg 0.44 2.2 0.92 0.35 0.38 0.56 1.9 1.7 0.43 0.037 1.1 0.34 46 66 0.45 0.4 0.057 0.079 0.011 0.085 0.0074 0.08 0.02 0.02 0.028 0.15 0.023 0.0039 0.043 0.04 0.0062 3.7 0.18 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S001 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:20 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 Sample  Bottom  Remediation  Depth Status (feet bgs) 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 6.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs VOCs Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8082 8082 8082 8082 8082 8082 8082 8315 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 1613B 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8330 8015B 8015B 8015B 8015B 314.0‐DI WET 9045C 9056 9056 9056 9056 9056 9056 9056 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 Analyte Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1016 Aroclor 1254 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1260 Formaldehyde DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran Heptachlorodibenzo‐p‐dioxins Heptachlorodibenzofurans Hexachlorodibenzo‐p‐dioxins Hexachlorodibenzofurans Pentachlorodibenzo‐p‐dioxins Pentachlorodibenzofurans Tetrachlorodibenzo‐p‐dioxins Tetrachlorodibenzofurans 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX sym‐Trinitrobenzene Tetryl C12‐C14 (Kerosene Range) C15‐C20 (Diesel Range) C21‐C30 (Lubricant Oil Range) C4‐C12 (Gasoline Range) Perchlorate pH Bromide Chloride Fluoride Nitrate‐N Nitrite‐NO2 Ortho Phosphate (as PO4) Sulfate Aluminum Antimony Beryllium Boron Lithium Potassium Sodium Zinc Zirconium Arsenic Page 107 of 108 CAS Number 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 12674112 11097691 11104282 11141165 53469219 12672296 11096825 50000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 35822469 67562394 55673897 39227286 70648269 57653857 57117449 19408743 72918219 40321764 57117416 60851345 57117314 1746016 51207319 3268879 39001020 37871004 38998753 34465468 55684941 36088229 30402154 41903575 55722275 99650 118967 6629294 121142 59229753 606202 35572782 88722 99081 19406510 99990 2691410 98953 55630 78115 121824 99354 479458 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) GRO C4‐C12 14797730 E‐10139 24959679 16887006 16984488 NO3N NO2 14265442 14808798 7429905 7440360 7440417 7440428 7439932 7440097 7440235 7440666 7440677 7440382 Result  Value 22 22 22 22 22 22 22 22 22 22 22 22 0.25 22 22 0.28 22 0.69 22 22 22 0.49 0.38 21 21 21 21 21 21 21 0.97 0.122 0.00647 0.0159 0.371 0.151 0.185 0.153 0.112 0.153 0.105 0.16 0.147 0.109 0.0946 0.111 0.103 0.106 0.122 8.46 0.281 0.784 0.151 0.155 0.118 0.109 0.0988 0.106 0.122 240 240 1000 240 1000 240 240 240 240 240 390 240 240 4800 3900 240 240 480 1.3 5.5 5.5 2.3 4.5 8 0.43 10 5.9 2.1 0.38 0.56 19 14000 0.42 1.1 5.6 18 1800 180 40 2.1 8.6 Result  Value  Units ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units SL Units 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.00025 mg/kg 0.022 mg/kg 0.022 mg/kg 0.00028 mg/kg 0.022 mg/kg 0.00069 mg/kg 0.022 mg/kg 0.022 mg/kg 0.022 mg/kg 0.00049 mg/kg 0.00038 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.021 mg/kg 0.67 mg/kg 0.000000122 mg/kg 6.47E‐09 mg/kg 1.59E‐08 mg/kg 0.000000371 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.000000846 mg/kg 0.000000122 mg/kg 0.00000846 mg/kg 0.00000846 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.00000423 mg/kg 0.000000846 mg/kg 0.000000122 mg/kg 0.24 mg/kg 0.24 mg/kg 1 mg/kg 0.24 mg/kg 1 mg/kg 0.24 mg/kg 0.24 mg/kg 0.24 mg/kg 0.24 mg/kg 0.24 mg/kg 0.39 mg/kg 0.24 mg/kg 0.24 mg/kg 4.8 mg/kg 3.9 mg/kg 0.24 mg/kg 0.24 mg/kg 0.48 mg/kg 1.3 mg/kg 5.5 mg/kg 5.5 mg/kg 2.3 mg/kg 0.0045 mg/kg 8 ph Units 5.6 mg/kg 10 mg/kg 5.9 mg/kg 2.1 mg/kg 5.6 mg/kg 5.6 mg/kg 19 mg/kg 14000 mg/kg 1.1 mg/kg 1.1 mg/kg 5.6 mg/kg 18 mg/kg 1800 mg/kg 180 mg/kg 40 mg/kg 2.1 mg/kg 8.6 mg/kg Detected N N N N N N N N N N N N Y N N Y N Y N N N Y Y N N N N N N N N Y Y Y Y N N N N N N N N N N N N N Y N N N N N N N N N Y N N N N N N N N N N N N N N N N N N Y N N Y N Y N Y Y Y N N Y Y N Y N Y Y Y Y Y Y Project  Qual  Code U U U U U U U U U U U U J U U J U J U U U J J U U U U U U U U J U U U U U U U U U U U U U J U U U U U U U U U J U U UJ U UJ U U U U U U U U U U U U U J U U J U J U Validation Note F, F, B, Original Result = 0.92 F, F, B, Original Result = 2.7 B B F, Original Result = 1.93 B B B B Q, Q, L Q, Q Q Q Q L, L J U U UJ U J Q, Q Q, Q F, F, F, Original Result = 1.3 B Boeing Soil Char Level  (mg/kg) 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 0.12 0.039 0.18 0.082 0.043 0.017 0.025 43 0.0000057 ‐‐ 0.000000563 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.92 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ ‐‐ 1400 1400 1400 1 0.5 ‐‐ ‐‐ ‐‐ 35 2340 ‐‐ 863.2 ‐‐ 37900 0.5 4.8 22 64.4 7524 754 153 10.64 24.2 Ratio Exceeds Boeing Boeing Soil Char Soil Char Level Level No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No SL No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No No No SL No SL No SL No SL No No SL No SL No SL No SL No No SL No SL No SL No No SL No SL No No No Yes No No SL No SL No SL No No No SL No No SL No Yes No No No No No No No No 9.57E‐03 4.89E‐03 2.00E‐01 1.69E‐03 6.77E‐01 3.02E‐03 4.15E‐04 2.00E‐02 6.67E‐02 1.00E‐02 5.68E‐02 5.68E‐01 6.46E‐04 2.97E‐03 5.68E‐02 2.33E‐04 1.95E‐01 1.28E‐05 2.47E‐02 5.68E‐02 1.51E‐03 3.77E‐04 3.17E‐04 1.75E‐01 5.38E‐01 1.17E‐01 2.56E‐01 4.88E‐01 1.24E+00 8.40E‐01 1.56E‐02 2.14E‐02 No SL 2.82E‐02 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 2.61E‐01 8.00E‐01 No SL No SL No SL No SL 8.00E‐01 No SL No SL No SL No SL 2.18E‐03 No SL No SL No SL 8.00E‐01 No SL No SL 9.29E‐04 3.93E‐03 3.93E‐03 2.30E+00 9.00E‐03 No SL No SL No SL 1.69E‐01 8.97E‐04 No SL 6.49E‐03 No SL 3.69E‐01 2.20E+00 2.29E‐01 2.55E‐01 2.80E‐01 2.39E‐01 2.39E‐01 2.61E‐01 1.97E‐01 3.55E‐01 SCL Basis Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Ecological RBSL Background Ecological RBSL MRL MRL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Background Background MRL Ecological RBSL Ecological RBSL Background Background Background Background Background Background SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL RL Units 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 21 21 21 21 21 21 21 0.67 4.23 4.23 4.23 4.23 4.23 4.23 4.23 4.23 4.23 4.23 4.23 4.23 4.23 0.846 0.846 8.46 8.46 4.23 4.23 4.23 4.23 4.23 4.23 0.846 0.846 240 240 1000 240 1000 240 240 240 240 240 390 240 240 4800 3900 240 240 480 5.5 5.5 5.5 5.5 4.5 0.1 5.6 5.6 5.6 5.6 5.6 5.6 5.6 11 1.1 0.56 5.6 7 110 130 5.6 28 0.56 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg MDL MDL  Units 0.33 0.52 0.96 0.36 0.51 0.29 0.34 0.18 0.19 0.15 0.16 0.16 0.16 0.22 0.14 0.21 0.27 0.23 0.25 0.27 0.36 0.35 0.2 5.4 5.9 17 5.5 9.7 6 2.8 0.3 ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.179 0.122 0.185 0.153 0.112 0.153 0.105 0.16 0.147 0.109 0.0946 0.111 0.103 0.106 0.0998 0.283 0.281 0.179 0.15 0.155 0.118 0.109 0.0988 0.106 0.0998 59 56 100 48 180 53 44 82 53 38 110 75 60 1600 1300 83 69 53 1.1 1.1 1.1 1.1 0.31 pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g pg/g ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg mg/kg mg/kg mg/kg ug/kg 0.43 2.2 0.92 0.35 0.38 0.56 1.9 1.7 0.42 0.037 1.1 0.34 46 66 0.44 0.4 0.057 mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Samples  Samples  Best  included in  included in  Pick? ERA HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Surface Soil Sample Object Name Sample Name (unique  Parent Sample  ID or unique  Name designation) SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 SWBS1006 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 ELSS01 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 SWBS1006S002 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 EL1S1 Sample ID ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 ELSS01S01 Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 9/16/08 13:30 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 5/23/96 0:00 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 10.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs VOCs Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Analysis  Method 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7196A 7471A 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8082 8082 8082 8082 8082 8082 8082 8315 9045 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 6010 7471 Analyte Barium Cadmium Chromium Cobalt Copper Lead Molybdenum Nickel Selenium Silver Thallium Vanadium Hexavalent Chromium Mercury bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1016 Aroclor 1254 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1260 Formaldehyde pH Aluminum Antimony Arsenic Barium Beryllium Cadmium Chromium Cobalt Copper Lead Molybdenum Nickel Selenium Silver Thallium Vanadium Zinc Mercury Only chemicals identified as COPCs/ROPCs in Tables E1‐1 and E1‐2 were included in HHRA risk calculations. Only chemicals identified as CPECs/RPECs in Tables E2‐2 and E2‐17 were included in ERA risk calculations. Page 108 of 108 CAS Number 7440393 7440439 7440473 7440484 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7440622 18540299 7439976 117817 85687 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 12674112 11097691 11104282 11141165 53469219 12672296 11096825 50000 E‐10139 7429905 7440360 7440382 7440393 7440417 7440439 7440473 7440484 7440508 7439921 7439987 7440020 7782492 7440224 7440280 7440622 7440666 7439976 Result  Value 88 0.21 21 7.6 12 7.3 0.18 15 0.83 0.031 0.27 45 0.2 0.0062 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 0.24 22 22 22 22 22 22 22 22 22 22 22 22 1.1 6.9 16100 7.5 56.9 109 0.78 0.21 22.5 8 11 11.3 1.1 13.1 0.45 0.73 0.39 40 73.2 0.04 Result  Value  Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg pH Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Result  in SL Units 88 0.21 21 7.6 12 7.3 0.18 15 0.83 0.031 0.27 45 0.56 0.034 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.00024 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.022 0.67 6.9 16100 7.5 56.9 109 0.78 0.21 22.5 8 11 11.3 1.1 13.1 0.45 0.73 0.39 40 73.2 0.04 SL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Detected Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y N Y N N N Y Y N Project  Qual  Code Validation Note J $, , , , B $, B J J B U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U U U U U U J F, F B H J Q F, F, B, Original Result = 8.2 F, F, Original Result = 0.22 F, F, B, Original Result = 1.5 F, F, B, Original Result = 3.7 F, Original Result = 0.4 B B B UJ U U U U B Boeing Soil Char Level  (mg/kg) 203.8 0.435 60.11 26.18 42 33.9 1.642 64.2 1 0.99 0.761 111.8 1.29 0.87 0.32 90 2.3 4.5 0.11 13 0.0325 7.29 53 1.1 0.33 2.2 0.387 0.0387 0.387 7.4 0.387 1.2 0.113 54 0.89 0.387 14.6 1.3 1.2 0.12 0.039 0.18 0.082 0.043 0.017 0.025 43 ‐‐ 37900 0.5 24.2 203.8 4.8 0.435 60.11 26.18 42 33.9 1.642 64.2 1 0.99 0.761 111.8 153 0.87 Exceeds Boeing Soil Char Level No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No SL No Yes Yes No No No No No No No No No No No No No No No Ratio Boeing Soil Char Level 4.32E‐01 4.83E‐01 3.49E‐01 2.90E‐01 2.86E‐01 2.15E‐01 1.10E‐01 2.34E‐01 8.30E‐01 3.13E‐02 3.55E‐01 4.03E‐01 4.34E‐01 3.91E‐02 6.88E‐02 2.44E‐04 9.57E‐03 4.89E‐03 2.00E‐01 1.69E‐03 6.77E‐01 3.02E‐03 4.15E‐04 2.00E‐02 6.67E‐02 1.00E‐02 5.68E‐02 5.68E‐01 5.68E‐02 2.97E‐03 5.68E‐02 1.83E‐02 1.95E‐01 4.44E‐06 2.47E‐02 5.68E‐02 1.51E‐03 1.69E‐02 1.83E‐02 1.83E‐01 5.64E‐01 1.22E‐01 2.68E‐01 5.12E‐01 1.29E+00 8.80E‐01 1.56E‐02 No SL 4.25E‐01 1.50E+01 2.35E+00 5.35E‐01 1.63E‐01 4.83E‐01 3.74E‐01 3.06E‐01 2.62E‐01 3.33E‐01 6.70E‐01 2.04E‐01 4.50E‐01 7.37E‐01 5.12E‐01 3.58E‐01 4.78E‐01 4.60E‐02 SCL Basis Background Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Suburban Residential RBSL Suburban Residential RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL Ecological RBSL MRL Ecological RBSL Ecological RBSL Background MRL Background Background Ecological RBSL Background Background Background Background Background Background Background MRL Ecological RBSL Suburban Residential RBSL Background Background Ecological RBSL SCL Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ph Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg RL 0.56 0.22 1.1 0.56 0.22 0.45 0.11 0.45 1.1 0.22 0.22 1.1 0.56 0.034 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 22 0.67 RL Units MDL mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.079 0.01 0.085 0.0074 0.079 0.02 0.02 0.028 0.15 0.023 0.0039 0.043 0.2 0.0062 3.6 0.18 0.32 0.51 0.95 0.35 0.5 0.28 0.34 0.18 0.19 0.15 0.16 0.16 0.16 0.22 0.14 0.21 0.27 0.23 0.25 0.27 0.36 0.34 0.19 5.5 6 17 5.6 9.9 6.1 2.9 0.3 MDL  Units Samples  Samples  Best  included in  included in  Pick? ERA HHRA mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg ug/kg mg/kg 0.45 mg/kg 0.73 mg/kg 0.39 mg/kg 0.04 mg/kg Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Object  Name ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV01 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV02 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 Sample Name  (unique ID or  unique  designation) RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV434 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV486 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV487 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 Parent Sample  Name Sample ID Sample Type ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV01S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV02S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S01 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/11/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 8 8 8 8 8 8 8 8 8 8 Sample  Bottom  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 8 8 8 8 8 8 8 8 8 8 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260M 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 Analyte CAS  Number Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene 1,1,2‐Trichloro‐1,2,2‐trifluoroethane m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene 1,1,2‐Trichloro‐1,2,2‐trifluoroethane m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene 1,1,2‐Trichloro‐1,2,2‐trifluoroethane m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 76131 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 76131 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 76131 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 Page 1 of 12 Result  Value 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 9.2 1 1 1 1 1.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 120 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 5.7 1 1 1 1 1 1 1 1 1 1 1 1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 9.2 1 1 1 1 1.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 120 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 5.7 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N Y N N N N Y N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N U U U U U U U U U UJ U U U U UJ U UJ U UJ U U U U UJ U U U U U U U UJ UJ U U U U U U U U U U U U U U U U U U U U U U UJ UJ U U U U U U U U U U U U U U U U U U U U U U UJ UJ C C C C C C C C C C C Boeing Soil  Vapor Char  Level (ug/L) 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 1210 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 1210 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 1210 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 Exceeds  Boeing  Soil  Vapor Char  Level No Yes No Yes Yes No No Yes Yes Yes No Yes No No Yes No No No No No Yes No Yes No Yes No Yes No Yes Yes No No Yes Yes Yes No Yes No No Yes No No No No No Yes No Yes No Yes No Yes No Yes Yes No No Yes Yes Yes No Yes No No Yes No No No No No Yes No Yes No Yes No Yes No Yes Yes No No Yes Yes Yes Ratio To  Boeing Soil  Vapor Char  Level 1.00E‐01 3.04E+00 4.00E‐03 2.38E+01 6.58E+00 6.58E‐01 1.27E‐01 8.62E+00 1.19E+01 1.73E+01 7.58E‐04 2.18E+00 4.00E‐02 9.62E‐03 1.03E+00 8.26E‐04 1.00E‐01 4.12E‐01 1.00E‐01 1.07E‐01 4.55E+00 4.00E‐02 1.55E+01 1.37E‐03 3.21E+01 1.00E‐01 3.04E+00 6.00E‐03 2.38E+01 6.58E+00 6.58E‐01 1.27E‐01 8.62E+00 1.19E+01 1.73E+01 7.58E‐04 2.18E+00 4.00E‐02 9.62E‐03 1.03E+00 8.26E‐04 1.00E‐01 4.12E‐01 1.00E‐01 1.07E‐01 4.55E+00 4.00E‐02 2.02E+02 1.37E‐03 3.21E+01 1.00E‐01 3.04E+00 4.00E‐03 2.38E+01 6.58E+00 6.58E‐01 1.27E‐01 8.62E+00 1.19E+01 1.73E+01 7.58E‐04 2.18E+00 4.00E‐02 9.62E‐03 1.03E+00 8.26E‐04 1.00E‐01 4.12E‐01 1.00E‐01 1.07E‐01 4.55E+00 4.00E‐02 9.61E+00 1.37E‐03 3.21E+01 1.00E‐01 3.04E+00 4.00E‐03 2.38E+01 6.58E+00 6.58E‐01 1.27E‐01 8.62E+00 1.19E+01 1.73E+01 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL RL Units 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA MDL 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 1 1 1 ug/L ug/L ug/L ug/L 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Gas Probe Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV03 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV08 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1003 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 Sample Name  (unique ID or  unique  designation) RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV488 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 RV733 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1003S050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 Parent Sample  Name ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 Sample ID Sample Type ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV03S02 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 ELSV08S01 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Collection  Date 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 7/17/97 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 9/29/99 0:00 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 13:03 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Sample  Bottom  Depth (feet bgs) 8 8 8 8 8 8 8 8 8 8 8 8 8 8 8 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene 1,1,2‐Trichloro‐1,2,2‐trifluoroethane m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene 75003 67663 156592 75718 100414 76131 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 630206 71556 79345 79005 76131 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 Page 2 of 12 Result  Value 1 1 1 1 1 1 1 1 1 1 1 1 11 1 1 2 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 5 1 1 1 1 1 1 1 0.54 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.13 0.1 0.1 0.1 0.1 0.1 0.12 0.43 5 0.11 0.1 0.95 0.1 0.1 0.1 0.5 0.1 0.22 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.17 5 0.05 0.1 0.17 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 1 1 1 1 1 1 1 1 1 1 1 11 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 5 1 1 1 1 1 1 1 0.54 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.13 0.1 0.1 0.1 0.1 0.1 0.12 0.43 5 0.11 0.1 0.95 0.1 0.1 0.1 0.5 0.1 0.22 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.17 5 0.05 0.1 0.17 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N Y N N N N N Y Y N Y N Y N N N N N Y N N N N N N N N N N N N N N Y N Y N Y U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ UJ U U U U C C U U U U U U U U U U U U U UJ U UJ U U U U U J U J U C C Boeing Soil  Vapor Char  Level (ug/L) 1320 0.459 25 104 0.973 1210 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1210 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 Exceeds  Boeing  Soil  Vapor Char  Level No Yes No No Yes No No No No No Yes No Yes No Yes No Yes No Yes Yes No No No Yes Yes Yes No Yes No No Yes No Yes No No Yes No Yes No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No Yes No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No Ratio To  Boeing Soil  Vapor Char  Level 7.58E‐04 2.18E+00 4.00E‐02 9.62E‐03 1.03E+00 8.26E‐04 1.00E‐01 4.12E‐01 1.00E‐01 1.07E‐01 4.55E+00 4.00E‐02 1.85E+01 1.37E‐03 3.21E+01 1.00E‐01 3.04E+00 4.00E‐03 2.38E+01 6.58E+00 8.26E‐04 6.58E‐01 1.27E‐01 8.62E+00 1.19E+01 1.73E+01 7.58E‐04 2.18E+00 4.00E‐02 9.62E‐03 1.03E+00 1.00E‐01 2.06E+00 1.00E‐01 1.07E‐01 4.55E+00 4.00E‐02 1.69E+00 1.37E‐03 3.21E+01 5.40E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.55E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.23E‐01 4.30E‐02 2.06E+00 1.10E‐02 1.07E‐02 4.32E+00 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.20E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.70E‐02 2.06E+00 5.00E‐03 1.07E‐02 7.73E‐01 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 5 1 1 1 1 1 1 1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA MDL 1 1 1 1 1 1 1 1 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 ug/L 1 ug/L 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N Y N N N N Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1004 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 Sample Name  (unique ID or  unique  designation) ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004D050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1004S100 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S01 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 Parent Sample  Name ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 ELSV1004S050 Sample ID Sample Type Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:26 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:18 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 3/26/08 11:06 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:33 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 Page 3 of 12 Result  Value 0.1 0.1 0.1 0.5 0.1 0.21 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.16 5 0.05 0.1 0.17 0.1 0.1 0.1 0.5 0.1 0.33 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.07 0.1 0.1 0.1 0.1 0.1 0.07 0.26 5 0.07 0.1 0.52 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 0.1 0.1 0.5 0.1 0.21 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.16 5 0.05 0.1 0.17 0.1 0.1 0.1 0.5 0.1 0.33 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.07 0.1 0.1 0.1 0.1 0.1 0.07 0.26 5 0.07 0.1 0.52 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N Y N N N N N N N N N N N N N N Y N Y N Y N N N N N Y N N N N N N N Y N N N N N Y Y N Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U UJ U UJ U U U U U J U J U C C U U U U U U U U U U U UJ J UJ U U U U J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U C C Boeing Soil  Vapor Char  Level (ug/L) 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 Exceeds  Boeing  Soil  Vapor Char  Level No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes No No No Yes No No No No No Yes No No No No No No Yes No No Yes No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes No No No Yes No Ratio To  Boeing Soil  Vapor Char  Level 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.10E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.60E‐02 2.06E+00 5.00E‐03 1.07E‐02 7.73E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 3.30E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 8.34E‐01 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 7.19E‐02 2.60E‐02 2.06E+00 7.00E‐03 1.07E‐02 2.36E+00 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1400 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 Sample Name  (unique ID or  unique  designation) ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1400S02 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401D01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 Parent Sample  Name ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 ELSV1401S01 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 11:35 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:52 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:43 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 Page 4 of 12 Result  Value 0.1 0.1 0.1 0.055 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.09 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.056 0.1 0.1 0.1 0.1 0.1 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 0.1 0.1 0.055 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.09 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.056 0.1 0.1 0.1 0.1 0.1 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N Y N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N U U U J U U U U U U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 Exceeds  Boeing  Soil  Vapor Char  Level No No No No Yes No No No No No No Yes No No No No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes No No No Yes No No No No No Yes No No No No No Ratio To  Boeing Soil  Vapor Char  Level 6.58E‐02 1.27E‐02 8.62E‐01 6.56E‐01 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.09E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 6.67E‐01 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1401 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1402 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 Sample Name  (unique ID or  unique  designation) ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1401S02 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S01 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1402S02 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 ELSV1403S01 Parent Sample  Name Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 4/28/08 10:44 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:35 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 9 9 9 9 9 9 9 9 9 9 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 Sample  Bottom  Depth (feet bgs) 10 10 10 10 10 10 10 10 10 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 Page 5 of 12 Result  Value 0.2 5 0.1 0.1 0.05 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.45 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.053 0.1 0.1 0.1 0.1 0.1 0.09 0.33 5 0.12 0.1 0.29 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.2 5 0.1 0.1 0.05 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.45 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.053 0.1 0.1 0.1 0.1 0.1 0.09 0.33 5 0.12 0.1 0.29 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N Y N N N N N Y Y N Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 Exceeds  Boeing  Soil  Vapor Char  Level No Yes No No No No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes No No No Yes No No No No No Yes No No No No No No Yes No No Yes No No No No Yes No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes Ratio To  Boeing Soil  Vapor Char  Level 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 2.27E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 4.50E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 6.32E‐01 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 9.25E‐02 3.30E‐02 2.06E+00 1.20E‐02 1.07E‐02 1.32E+00 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 3.21E+00 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV1403 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2000 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 Sample Name  (unique ID or  unique  designation) ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV1403S02 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2000S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S001 ELSV2001S002 ELSV2001S002 Parent Sample  Name Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 5/16/08 11:00 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:23 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 7:45 8/5/13 8:02 8/5/13 8:02 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 8.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9.3 9.3 Sample  Bottom  Depth (feet bgs) 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 9.8 9.8 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 Page 6 of 12 Result  Value 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.3 0.1 0.5 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.3 0.1 0.5 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 Exceeds  Boeing  Soil  Vapor Char  Level No No No Yes No No No No Yes Yes No No No No No No Yes No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No Ratio To  Boeing Soil  Vapor Char  Level 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 1.19E+00 1.73E+00 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 2.06E+00 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 5.06E‐01 1.37E‐04 4.13E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.2 5 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.1 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 2.5 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2001 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2002 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 ELSV2003 Sample Name  (unique ID or  unique  designation) ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2001S002 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2002S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 ELSV2003S001 Parent Sample  Name Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/5/13 8:02 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/7/13 7:34 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 8/5/13 11:40 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 9.3 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 9.8 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 Page 7 of 12 Result  Value 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 Exceeds  Boeing  Soil  Vapor Char  Level No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes Ratio To  Boeing Soil  Vapor Char  Level 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2004 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2006 ELSV2008 ELSV2008 Sample Name  (unique ID or  unique  designation) ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2004S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2006S001SP ELSV2008S001 ELSV2008S001 Parent Sample  Name ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 ELSV2006S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Split Sample Primary Sample Primary Sample Collection  Date 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 8:57 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:08 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/5/13 13:11 8/7/13 7:16 8/7/13 7:16 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 9.5 9.5 Sample  Bottom  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Analytical  Class VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 TO‐15 8260B 8260B Analyte Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene Methylene chloride m‐Xylene & p‐Xylene o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol Page 8 of 12 CAS  Number Result  Value Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code 1330207 0.1 ug/L 67630 5 ug/L 630206 0.1 ug/L 71556 0.1 ug/L 79345 0.1 ug/L 79005 0.25 ug/L 76131 0.1 ug/L 75343 0.1 ug/L 75354 0.1 ug/L 95501 0.1 ug/L 107062 0.1 ug/L 142289 0.1 ug/L 106467 0.1 ug/L 71432 0.1 ug/L 56235 0.1 ug/L 75003 0.25 ug/L 67663 0.1 ug/L 156592 0.1 ug/L 75718 0.1 ug/L 100414 0.1 ug/L 179601231 0.1 ug/L 75092 0.1 ug/L 95476 0.1 ug/L 127184 0.25 ug/L 108883 0.1 ug/L 156605 0.1 ug/L 79016 0.1 ug/L 75694 0.1 ug/L 75014 0.1 ug/L 1330207 0.1 ug/L 67630 5 ug/L 630206 0.1 ug/L 71556 0.1 ug/L 79345 0.1 ug/L 79005 0.25 ug/L 76131 0.1 ug/L 75343 0.1 ug/L 75354 0.1 ug/L 95501 0.1 ug/L 107062 0.1 ug/L 142289 0.1 ug/L 106467 0.1 ug/L 71432 0.1 ug/L 56235 0.1 ug/L 75003 0.25 ug/L 67663 0.1 ug/L 156592 0.1 ug/L 75718 0.1 ug/L 100414 0.1 ug/L 179601231 0.1 ug/L 75092 0.1 ug/L 95476 0.1 ug/L 127184 0.25 ug/L 108883 0.1 ug/L 156605 0.1 ug/L 79016 0.1 ug/L 75694 0.1 ug/L 75014 0.1 ug/L 1330207 0.0085 ug/L 630206 0.0069 ug/L 71556 0.0016 ug/L 79345 0.0069 ug/L 76131 0.02 ug/L 79005 0.0055 ug/L 75343 0.004 ug/L 75354 0.004 ug/L 107062 0.004 ug/L 71432 0.0032 ug/L 56235 0.0063 ug/L 75003 0.0026 ug/L 67663 0.0021 ug/L 156592 0.004 ug/L 75718 0.0014 ug/L 100414 0.0025 ug/L 75092 0.0035 ug/L 179601231 0.0058 ug/L 95476 0.0027 ug/L 127184 0.0095 ug/L 108883 0.00089 ug/L 156605 0.004 ug/L 79016 0.0054 ug/L 75694 0.02 ug/L 75014 0.0026 ug/L 1330207 0.1 ug/L 67630 5 ug/L 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.0085 0.0069 0.0016 0.0069 0.02 0.0055 0.004 0.004 0.004 0.0032 0.0063 0.0026 0.0021 0.004 0.0014 0.0025 0.0035 0.0058 0.0027 0.0095 0.00089 0.004 0.0054 0.02 0.0026 0.1 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y N Y N N N N N N N Y N Y Y N Y Y Y Y N N Y N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U U U U U U U U J U J J U J J U U U U U Boeing Soil  Vapor Char  Level (ug/L) 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 1210 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 2.43 10 10 9.36 0.22 25 0.593 730 0.0312 10 7300 Exceeds  Boeing  Soil  Vapor Char  Level No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No Ratio To  Boeing Soil  Vapor Char  Level 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 8.50E‐04 2.10E‐02 6.40E‐06 1.64E‐01 1.65E‐05 3.62E‐02 2.63E‐03 5.06E‐04 3.45E‐02 3.81E‐02 1.09E‐01 1.97E‐06 4.58E‐03 1.60E‐04 1.35E‐05 2.57E‐03 1.44E‐03 5.80E‐04 2.70E‐04 1.01E‐03 4.05E‐03 1.60E‐04 9.11E‐03 2.74E‐05 8.33E‐02 1.00E‐02 6.85E‐04 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.0043 0.0069 0.0055 0.0069 0.015 0.0055 0.004 0.004 0.004 0.0032 0.0063 0.0026 0.0049 0.004 0.0049 0.0043 0.0035 0.0043 0.0043 0.0068 0.0038 0.004 0.0054 0.0056 0.0026 0.1 5 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.00087 0.0014 0.0011 0.0014 0.0038 0.0011 0.00081 0.00079 0.00081 0.00064 0.0013 0.00053 0.00098 0.00079 0.00099 0.00087 0.00069 0.00087 0.00087 0.0014 0.00075 0.00079 0.0011 0.0011 0.00051 0.054 1 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N Y N N N N N N N Y N Y Y N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2008 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2009 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 ELSV2011 Sample Name  (unique ID or  unique  designation) ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2008S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2009S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 ELSV2011S001 Parent Sample  Name Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/7/13 7:16 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 9:37 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 8/5/13 8:22 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 Page 9 of 12 Result  Value 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 Exceeds  Boeing  Soil  Vapor Char  Level No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes Ratio To  Boeing Soil  Vapor Char  Level 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2012 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 ELSV2013 Sample Name  (unique ID or  unique  designation) ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2012S001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013D001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 Parent Sample  Name ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 ELSV2013S001 Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Field Duplicate Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 10:53 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 8/5/13 9:59 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 Page 10 of 12 Result  Value 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 Exceeds  Boeing  Soil  Vapor Char  Level No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No Ratio To  Boeing Soil  Vapor Char  Level 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV2013 ELSV2013 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2014 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2016 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV2018 Sample Name  (unique ID or  unique  designation) ELSV2013S001 ELSV2013S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2014S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2016S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 Parent Sample  Name Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 8/5/13 9:59 8/5/13 9:59 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 11:18 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 10:23 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Sample  Bottom  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Other SVOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 67630 630206 71556 79345 79005 76131 75343 75354 95501 107062 142289 106467 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 Page 11 of 12 Result  Value 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 1.5 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Boeing Soil  Vapor Char  Level (ug/L) 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 7300 0.329 250 0.042 0.152 1210 1.52 7.9 66 0.116 ‐‐ ‐‐ 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 Exceeds  Boeing  Soil  Vapor Char  Level No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No No No No Yes No No No No Yes Yes No No No No No No SL No SL Yes Yes No No No No No No No No No No Ratio To  Boeing Soil  Vapor Char  Level 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 1.24E‐03 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 1.00E‐02 6.85E‐04 3.04E‐01 4.00E‐04 2.38E+00 1.64E+00 8.26E‐05 6.58E‐02 1.27E‐02 1.52E‐03 8.62E‐01 No SL No SL 1.19E+00 1.73E+00 1.89E‐04 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.00E‐02 4.12E‐02 1.00E‐02 2.67E‐02 4.55E‐01 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 5 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 0.1 0.1 0.1 0.1 0.1 0.1 0.25 0.1 RL Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 0.047 0.07 0.026 0.072 0.054 1 0.043 0.028 0.054 0.11 0.044 0.031 0.076 0.048 0.048 0.041 0.041 0.015 0.041 0.13 0.031 0.044 0.07 0.031 0.054 0.05 0.043 0.1 0.028 Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL No Soil Vapor CL Soil Vapor APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Soil Vapor Sample Object  Name ELSV2018 ELSV2018 ELSV2018 ELSV2018 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 ELSV3000 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 SWSV1006 Sample Name  (unique ID or  unique  designation) ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV2018S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 ELSV3000S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S001 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 SWSV1006S002 Parent Sample  Name Sample ID Sample Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Collection  Date 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 8/5/13 13:38 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 5/23/14 7:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:48 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 9/25/08 12:33 Matrix  Type Sample Top  Depth (feet bgs) Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 9 Sample  Bottom  Depth (feet bgs) 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical  Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte CAS  Number trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Benzene Carbon Tetrachloride Chloroethane Chloroform cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride 156605 79016 75694 75014 1330207 630206 71556 79345 79005 76131 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 1330207 630206 71556 79345 79005 75343 75354 107062 71432 56235 75003 67663 156592 75718 100414 179601231 75092 95476 127184 108883 156605 79016 75694 76131 75014 Only chemicals identified as COPCs/ROPCs in Tables E1‐1 and E1‐2 were included in HHRA risk calculations. Only chemicals identified as CPECs/RPECs in Tables E2‐2 and E2‐17 were included in ERA risk calculations Page 12 of 12 Result  Value 0.1 0.1 0.1 0.1 0.04 0.02 0.02 0.02 0.02 0.061 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.014 0.04 0.02 0.02 0.02 0.023 0.02 0.02 0.022 0.02 0.27 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.05 0.05 0.1 0.1 0.1 0.1 0.1 0.19 2 0.08 0.1 0.05 0.1 0.1 0.1 0.5 0.05 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.05 0.05 0.1 0.1 0.1 0.1 0.1 0.2 2 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.05 Result  Project  Result in  Value  SL Units Detected Qual  Validation Note SL Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.1 0.1 0.1 0.1 0.04 0.02 0.02 0.02 0.02 0.061 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.014 0.04 0.02 0.02 0.02 0.02 0.02 0.02 0.022 0.02 0.27 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.05 0.05 0.1 0.1 0.1 0.1 0.1 0.19 2 0.08 0.1 0.05 0.1 0.1 0.1 0.5 0.05 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.05 0.05 0.1 0.1 0.1 0.1 0.1 0.2 2 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.05 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N Y N N N N Y N N N N N N N N N Y Y N N N N N N Y N Y N N N N N N N N N N N N N N Y N Y N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U UJ J U U U U U U U U U U U U U U U U U U U U U J U J U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U L, L L B Boeing Soil  Vapor Char  Level (ug/L) 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1210 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 10 0.329 250 0.042 0.152 1.52 7.9 0.116 0.0839 0.0579 1320 0.459 25 104 0.973 10 2.43 10 9.36 0.22 25 0.593 730 1210 0.0312 Exceeds  Boeing  Soil  Vapor Char  Level No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No No No No No No No No No No No Yes No No No Yes No No No No No No No No No No No No No No No No No No No No Yes Ratio To  Boeing Soil  Vapor Char  Level 4.00E‐03 1.69E‐01 1.37E‐04 3.21E+00 4.00E‐03 6.08E‐02 8.00E‐05 4.76E‐01 1.32E‐01 5.04E‐05 1.32E‐02 2.53E‐03 1.72E‐01 2.38E‐01 3.45E‐01 1.52E‐05 4.36E‐02 8.00E‐04 1.92E‐04 1.44E‐02 4.00E‐03 8.23E‐03 2.00E‐03 2.14E‐03 9.09E‐02 8.00E‐04 3.37E‐02 3.01E‐05 6.41E‐01 2.70E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 5.96E‐01 8.64E‐01 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 1.90E‐02 8.23E‐01 8.00E‐03 1.07E‐02 2.27E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 1.60E+00 2.00E‐02 3.04E‐01 4.00E‐04 4.76E+00 6.58E‐01 6.58E‐02 1.27E‐02 8.62E‐01 5.96E‐01 8.64E‐01 7.58E‐05 2.18E‐01 4.00E‐03 9.62E‐04 1.03E‐01 2.00E‐02 8.23E‐01 1.00E‐02 1.07E‐02 4.55E‐01 4.00E‐03 1.69E‐01 1.37E‐04 4.13E‐04 1.60E+00 SVCL  Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL 0.1 0.1 0.1 0.1 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.05 0.05 0.1 0.1 0.1 0.1 0.1 0.2 2 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.05 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.05 0.05 0.1 0.1 0.1 0.1 0.1 0.2 2 0.1 0.1 0.1 0.1 0.1 0.1 0.5 0.05 RL Units MDL Samples  Samples  MDL  Best  included in  included in  Units Pick? ERA HHRA ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.047 0.07 0.026 0.072 0.0089 0.009 0.0054 0.0089 0.0063 0.012 0.0062 0.0072 0.011 0.0041 0.012 0.016 0.006 0.0094 0.011 0.003 0.008 0.01 0.0089 0.0053 0.0043 0.0039 0.012 0.0053 0.01 0.1 0.05 0.05 0.1 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 1 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 0.1 0.05 0.05 0.1 0.05 0.05 0.05 0.05 0.036 0.025 0.05 0.05 0.05 0.05 0.05 0.1 1 0.05 0.05 0.05 0.05 0.05 0.05 0.25 0.013 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Sediment APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Sediment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Sample Name  Sample  Parent  Sample Top  Result  Project  Boeing  Exceeds Boeing  Ratio To Boeing  Samples  Samples  Object  Object  (unique ID or  Sample  Sample  Collection  Matrix  Bottom  Remediation  Result  Analytical  Analysis  CAS  Result  Result in  Validation  MDL  Best  Sample  Depth Analyte Value  SL Units Detected Qual  Sediment Char  Sediment Char  Sediment Char  RL RL Units MDL included  included  Type Name unique  ID Type Date Type Depth Status Type Class Method Number Value SL Units Note Units Pick? Name (feet bgs) Units Code Level (mg/kg) Level Level in ERA in HHRA designation) (feet bgs) None Only chemicals identified as COPCs/ROPCs in Tables E1‐1 and E1‐2 were included in HHRA risk calculations. Only chemicals identified as CPECs/RPECs in Tables E2‐2 and E2‐17 were included in ERA risk calculations. Page 1 of 1 Surface Water APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Surface Water RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Exceeds  Ratio To  Boeing  Sample Name  Sample  Samples  Samples  Parent  Sample Top  Result  Project  Boeing  Boeing  SWCL  MDL  Best  Object  Object  (unique ID or  Sample  Sample  Collection  Matrix  Bottom  Remediation  Result  Analytical  Analysis  CAS  Result  Result in  Validation  Surfacewater  RL RL Units MDL included  included  Sample  Depth Analyte Value  SL Units Detected Qual  Char Level  Surfacewater  Surfacewater  Units Units Pick? Type Name unique  ID Type Date Type Depth Status Type Class Method Number Value SL Units Note in ERA in HHRA Name (feet bgs) Units Code (mg/L) Char Level Char Level designation) (feet bgs) No data Only chemicals identified as COPCs/ROPCs in Tables E1‐1 and E1‐2 were included in HHRA risk calculations. Only chemicals identified as CPECs/RPECs in Tables E2‐2 and E2‐17 were included in ERA risk calculations. Page 1 of 1 Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 ACID‐69 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 BASE‐75 COMMON‐281 COMMON‐281 COMMON‐281 COMMON‐281 COMMON‐281 COMMON‐281 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 COMMON‐283 RS‐17 (5/3/1998) RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 Sample ID Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 9/12/87 0:00 5/3/98 0:00 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 Matrix  Type Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Sample Top  Depth (feet bgs) 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 6.4 Sample  Bottom  Depth (feet bgs) 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Energetics Energetics Energetics Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Metals Metals Metals Metals Metals Metals Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Inorganics VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 625 Metals Metals Metals Metals Metals Metals Anions/Cations Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Metals Metals Metals Metals Metals Metals Inorganics 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chlorophenol 2‐Nitrophenol 4,6‐Dinitro‐o‐cresol 4‐Nitrophenol p‐Chloro‐m‐cresol Pentachlorophenol Phenol 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2‐Chloronaphthalene 3,3'‐Dichlorobenzidine 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether Benzidine bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine Benzo(b)fluoranthene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Boron, Dissolved Calcium, Dissolved Magnesium, Dissolved Potassium, Dissolved Silica, Dissolved Sodium, Dissolved Chloride Bicarbonate Carbonate Fluoride Nitrate‐NO3 Sulfate Total Dissolved Solids Boron, Dissolved Calcium, Dissolved Magnesium, Dissolved Potassium, Dissolved Silica, Dissolved Sodium, Dissolved Perchlorate Xylenes, Total 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Acetone Benzene Carbon Tetrachloride Chloroform cis‐1,2‐Dichloroethene Ethylbenzene Methyl ethyl ketone Methylene chloride m‐Xylene & p‐Xylene o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Page 1 of 9 CAS Number 88062 120832 105679 51285 95578 88755 534521 100027 59507 87865 108952 121142 606202 98953 120821 122667 91587 91941 101553 7005723 92875 111911 111444 108601 117817 85687 84662 131113 84742 117840 118741 87683 77474 67721 78591 62759 621647 86306 205992 83329 208968 120127 56553 50328 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 7440428‐D 7440702‐D 7439954‐D 7440097‐D 7631869‐D 7440235‐D 16887006 71523 3812326 16984488 NO3 14808798 E‐10173 7440428‐D 7440702‐D 7439954‐D 7440097‐D 7631869‐D 7440235‐D 14797730 1330207 71556 76131 79005 75343 75354 107062 67641 71432 56235 67663 156592 100414 78933 75092 179601231 95476 127184 108883 156605 Result  Value 10 10 10 25 10 10 50 25 10 10 10 10 10 10 10 10 10 10 10 10 40 10 10 10 10 10 10 25 50 10 10 10 10 10 10 80 40 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 0.25 128 20 5.9 32 123 172 373 0 0.31 19.9 208 940 0.1 155 18 0.7 34 144 4 0.34 0.16 0.42 0.27 0.22 0.23 0.13 1.9 0.16 0.19 0.16 0.15 0.16 2 0.32 0.34 0.19 0.2 0.17 0.15 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 10 10 10 25 10 10 50 25 10 10 10 10 10 10 10 10 10 10 10 10 40 10 10 10 10 10 10 25 50 10 10 10 10 10 10 80 40 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 250 128000 20000 5900 32000 123000 172000 373000 0 310 19900 208000 940000 100 155000 18000 700 34000 144000 4 2 1 5 1 1 1 0.5 10 1 1 1 1 1 10 5 2 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y Y Y Y Y Y N Y Y Y Y N Y Y Y Y Y N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 2.1 Yes 4.76E+00 ug/L ‐‐ No SL No SL ug/L 100 No 1.00E‐01 ug/L ‐‐ No SL No SL ug/L 63 No 1.59E‐01 ug/L ‐‐ No SL No SL ug/L 1.3 Yes 3.85E+01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 1 Yes 1.00E+01 ug/L 4200 No 2.38E‐03 ug/L ‐‐ No SL No SL ug/L 0.22 Yes 4.55E+01 ug/L 110 No 9.09E‐02 ug/L 5 Yes 2.00E+00 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 0.12 Yes 8.33E+01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 0.0003 Yes 1.33E+05 ug/L 38 No 2.63E‐01 ug/L 360 No 2.78E‐02 ug/L ‐‐ No SL No SL ug/L 4 Yes 2.50E+00 ug/L 78 No 1.28E‐01 ug/L 10000 No 1.00E‐03 ug/L 130000 No 1.92E‐04 ug/L 1300 No 3.85E‐02 ug/L 500 No 2.00E‐02 ug/L 1 Yes 1.00E+01 ug/L ‐‐ No SL No SL ug/L 50 No 2.00E‐01 ug/L 10 No 1.00E+00 ug/L 5400 No 1.85E‐03 ug/L 0.01 Yes 8.00E+03 ug/L 0.01 Yes 4.00E+03 ug/L 16 No 6.25E‐01 ug/L ‐‐ No SL No SL ug/L 380 No 2.63E‐02 ug/L 380 No 2.63E‐02 ug/L 3800 No 2.63E‐03 ug/L ‐‐ No SL No SL ug/L 0.2 Yes 5.00E+01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 250 No 4.00E‐02 ug/L 250 No 4.00E‐02 ug/L ‐‐ No SL No SL ug/L 17 No 5.88E‐01 ug/L 3800 No 2.63E‐03 ug/L 380 No 2.63E‐02 ug/L 340 No 7.35E‐01 ug/L ‐‐ No SL No SL ug/L 77000 No 2.60E‐01 ug/L 9600 No 6.15E‐01 ug/L ‐‐ No SL No SL ug/L 190000 No 6.47E‐01 ug/L 250000 No 6.88E‐01 ug/L No SL No SL ug/L ‐‐ ‐‐ No SL No SL ug/L 800 No 3.88E‐01 ug/L 45000 No 4.42E‐01 ug/L ug/L 376000 No 5.53E‐01 500000 Yes 1.88E+00 ug/L 340 No 2.94E‐01 ug/L ‐‐ No SL No SL ug/L 77000 No 2.34E‐01 ug/L 9600 No 7.29E‐02 ug/L ‐‐ No SL No SL ug/L 190000 No 7.58E‐01 ug/L 6 No 6.67E‐01 ug/L 1750 No 1.14E‐03 ug/L 200 No 5.00E‐03 ug/L 1200 No 4.17E‐03 ug/L 5 No 2.00E‐01 ug/L 5 No 2.00E‐01 ug/L 6 No 1.67E‐01 ug/L 0.5 No 1.00E+00 ug/L 20000 No 5.00E‐04 ug/L 1 No 1.00E+00 ug/L 0.5 Yes 2.00E+00 ug/L 80 No 1.25E‐02 ug/L 6 No 1.67E‐01 ug/L 300 No 3.33E‐03 ug/L 3800 No 2.63E‐03 ug/L 5 No 1.00E+00 ug/L 1750 No 1.14E‐03 ug/L 1750 No 5.71E‐04 ug/L 5 No 2.00E‐01 ug/L 150 No 6.67E‐03 ug/L 10 No 1.00E‐01 ug/L RL RL Units MDL Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 2 1 5 1 1 1 0.5 10 1 1 1 1 1 10 5 2 1 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 4 0.34 0.16 0.42 0.27 0.22 0.23 0.13 1.9 0.16 0.19 0.16 0.15 0.16 2 0.32 0.34 0.19 0.2 0.17 0.15 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐17 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐17_011311_01 RS‐17_011311_01 RS‐17_011311_01 RS‐17_022603_01 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 Trace‐24 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2860 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 VOC‐2861 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_012115_01 RS‐37_021014_01A RS‐37_021014_01A Sample ID Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 1/13/11 10:50 1/13/11 10:50 1/13/11 10:50 2/26/03 12:07 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 6/13/85 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 12/5/92 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 3/4/93 0:00 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 1/21/15 9:31 2/10/14 8:46 2/10/14 8:46 Matrix  Type Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Sample Top  Depth (feet bgs) 6.4 6.4 6.4 6 Sample  Bottom  Depth (feet bgs) 16 16 16 16 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Hydrocarbons Hydrocarbons Analysis  Method 8260B 8260B 8260B 314.0 Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8010 8321A 8321A 8321A 8321A 8321A 8321A 8321A 8321A 8321A 8321A 8015B 8015B Analyte Trichloroethene Trichlorofluoromethane Vinyl chloride Perchlorate Antimony, Dissolved Arsenic, Dissolved Barium, Dissolved Beryllium, Dissolved Cadmium, Dissolved Chromium, Dissolved Copper, Dissolved Iron, Dissolved Lead, Dissolved Manganese, Dissolved Mercury, Dissolved Molybdenum, Dissolved Nickel, Dissolved Selenium, Dissolved Silver, Dissolved Strontium, Dissolved Thallium, Dissolved Zinc, Dissolved 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dichlorodifluoromethane Methylene chloride Tetrachloroethene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Vinyl chloride 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene 2‐Chloroethylvinyl ether Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dichlorodifluoromethane Methylene chloride Tetrachloroethene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb MCPA MCPP Diesel Range Organics (C12‐C14) Diesel Range Organics (C15‐C20) Page 2 of 9 CAS Number 79016 75694 75014 14797730 7440360‐D 7440382‐D 7440393‐D 7440417‐D 7440439‐D 7440473‐D 7440508‐D 7439896‐D 7439921‐D 7439965‐D 7439976‐D 7439987‐D 7440020‐D 7782492‐D 7440224‐D 7440246‐D 7440280‐D 7440666‐D 71556 79345 79005 75343 75354 95501 107062 78875 541731 106467 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 75718 75092 127184 156605 10061026 79016 75694 76131 75014 71556 79345 79005 75343 75354 95501 107062 78875 541731 106467 110758 75274 75252 74839 56235 108907 75003 67663 74873 156592 10061015 124481 75718 75092 127184 156605 10061026 79016 75694 75014 93765 93721 94757 94826 75990 1918009 120365 88857 94746 93652 EFHD (C12‐C14) EFHD (C15‐C20) Result  Value 0.16 0.29 0.1 0.8 1 0.01 0.5 0.05 0.005 0.01 0.01 0.05 0.01 0.01 0.0002 0.1 0.05 0.005 0.01 0.4 0.5 0.01 0.2 0.2 0.2 0.2 0.3 0.5 0.2 0.2 0.5 0.5 0.2 1 1 0.2 0.5 1 0.2 1 0.2 0.2 0.2 1 2 0.2 0.2 0.2 3 2 0.2 0.2 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 3 0.5 0.5 0.5 0.5 4.5 0.5 0.5 0.57 0.43 0.51 1.2 1.8 0.85 0.5 0.36 0.42 0.47 0.095 0.095 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L 1 1 1 4 1000 10 500 50 5 10 10 50 10 10 0.2 100 50 5 10 400 500 10 0.2 0.2 0.2 0.2 0.3 0.5 0.2 0.2 0.5 0.5 0.2 1 1 0.2 0.5 1 0.2 1 0.2 0.2 0.2 1 2 0.2 0.2 0.2 3 2 0.2 0.2 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 3 0.5 0.5 0.5 0.5 4.5 0.5 0.5 5 5 5 5 5 5 5 5 5 5 240 240 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N Y N N N N N N Y N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N Validation Note U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ UJ U U U U UJ U U C CQ C Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 5 No 2.00E‐01 ug/L 150 No 6.67E‐03 ug/L 0.5 Yes 2.00E+00 ug/L 6 No 6.67E‐01 ug/L 2.5 Yes 4.00E+02 ug/L 7.7 Yes 1.30E+00 ug/L 150 Yes 3.33E+00 ug/L 0.14 Yes 3.57E+02 ug/L 0.2 Yes 2.50E+01 ug/L 14 No 7.14E‐01 ug/L 4.7 Yes 2.13E+00 ug/L 4100 No 1.22E‐02 ug/L 11 No 9.09E‐01 ug/L 150 No 6.67E‐02 ug/L 0.063 Yes 3.17E+00 ug/L 2.2 Yes 4.55E+01 ug/L 17 Yes 2.94E+00 ug/L 1.6 Yes 3.13E+00 ug/L 0.17 Yes 5.88E+01 ug/L 800 No 5.00E‐01 ug/L 0.13 Yes 3.85E+03 ug/L 6300 No 1.59E‐03 ug/L 200 No 1.00E‐03 ug/L 1 No 2.00E‐01 ug/L 5 No 4.00E‐02 ug/L 5 No 4.00E‐02 ug/L 6 No 5.00E‐02 ug/L 600 No 8.33E‐04 ug/L 0.5 No 4.00E‐01 ug/L 5 No 4.00E‐02 ug/L 600 No 8.33E‐04 ug/L 5 No 1.00E‐01 ug/L 80 No 2.50E‐03 ug/L 80 No 1.25E‐02 ug/L 8.8 No 1.14E‐01 ug/L 0.5 No 4.00E‐01 ug/L 70 No 7.14E‐03 ug/L 16 No 6.25E‐02 ug/L 80 No 2.50E‐03 ug/L 5.7 No 1.75E‐01 ug/L 6 No 3.33E‐02 ug/L 0.5 No 4.00E‐01 ug/L 80 No 2.50E‐03 ug/L 1000 No 1.00E‐03 ug/L 5 No 4.00E‐01 ug/L 5 No 4.00E‐02 ug/L 10 No 2.00E‐02 ug/L 0.81 No 2.47E‐01 ug/L 5 No 6.00E‐01 ug/L 150 No 1.33E‐02 ug/L 1200 No 1.67E‐04 ug/L 0.5 No 4.00E‐01 ug/L 200 No 2.50E‐03 ug/L 1 No 5.00E‐01 ug/L 5 No 1.00E‐01 ug/L 5 No 1.00E‐01 ug/L 6 No 8.33E‐02 ug/L 600 No 8.33E‐04 ug/L 0.5 No 1.00E+00 ug/L 5 No 1.00E‐01 ug/L 600 No 8.33E‐04 ug/L 5 No 1.00E‐01 ug/L ‐‐ No SL No SL ug/L 80 No 6.25E‐03 ug/L ug/L 80 No 6.25E‐03 8.8 No 5.68E‐02 ug/L 0.5 No 1.00E+00 ug/L 70 No 7.14E‐03 ug/L 16 No 3.13E‐02 ug/L 80 No 6.25E‐03 ug/L 5.7 No 8.77E‐02 ug/L 6 No 8.33E‐02 ug/L 0.5 No 1.00E+00 ug/L 80 No 6.25E‐03 ug/L 1000 No 3.00E‐03 ug/L 5 No 1.00E‐01 ug/L 5 No 1.00E‐01 ug/L 10 No 5.00E‐02 ug/L 0.81 No 6.17E‐01 ug/L 5 No 9.00E‐01 ug/L 150 No 3.33E‐03 ug/L 0.5 No 1.00E+00 ug/L 130 No 3.85E‐02 ug/L ‐‐ No SL No SL ug/L 130 No 3.85E‐02 ug/L 100 No 5.00E‐02 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 7 No 7.14E‐01 ug/L 6.3 No 7.94E‐01 ug/L 13 No 3.85E‐01 ug/L 100 Yes 2.40E+00 ug/L 100 Yes 2.40E+00 ug/L RL RL Units 1 1 1 4 ug/L ug/L ug/L ug/L MDL 0.16 0.29 0.1 0.8 Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.5 ug/L Y Y Y Y Y Y Y 0.5 ug/L 0.5 ug/L Y Y Y Y Y Y 1 ug/L Y 2 ug/L 0.2 ug/L Y 0.5 ug/L Y Y Y Y Y Y Y Y 0.5 ug/L 0.5 ug/L Y Y Y Y Y Y 3 ug/L Y 0.5 ug/L 5 5 5 5 5 5 5 5 5 5 0.24 0.24 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L 0.57 0.43 0.51 1.2 1.8 0.85 0.5 0.36 0.42 0.47 0.095 0.095 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name Sample ID Sample Type Collection Date Matrix  Type Sample Top  Depth (feet bgs) Sample  Bottom  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Hydrocarbons Hydrocarbons Hydrocarbons Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 8015B 8015B 8015B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7470A 7470A 8270C SIM 8270C SIM Diesel Range Organics (C21‐C30) Gasoline Range Organics (C8‐C11) Diesel Range Organics (C8‐C30) Lithium Lithium, Dissolved Sodium Sodium, Dissolved Antimony Antimony, Dissolved Arsenic Arsenic, Dissolved Barium Barium, Dissolved Beryllium Beryllium, Dissolved Cadmium Cadmium, Dissolved Chromium Chromium, Dissolved Copper Copper, Dissolved Lead Lead, Dissolved Molybdenum Molybdenum, Dissolved Nickel Nickel, Dissolved Selenium Selenium, Dissolved Silver Silver, Dissolved Thallium Thallium, Dissolved Vanadium Vanadium, Dissolved Zinc Zinc, Dissolved Mercury Mercury, Dissolved bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate EFHD (C21‐C30) EFHD (C8‐C11) EFHD (C8‐C30) 7439932 7439932‐D 7440235 7440235‐D 7440360 7440360‐D 7440382 7440382‐D 7440393 7440393‐D 7440417 7440417‐D 7440439 7440439‐D 7440473 7440473‐D 7440508 7440508‐D 7439921 7439921‐D 7439987 7439987‐D 7440020 7440020‐D 7782492 7782492‐D 7440224 7440224‐D 7440280 7440280‐D 7440622 7440622‐D 7440666 7440666‐D 7439976 7439976‐D 117817 85687 EEL EEL EEL CC 1 EEL CC 1 Groundwater Monitoring Well RS‐37 Groundwater Monitoring Well RS‐37 RS‐37_021014_01A RS‐37_021014_01A Primary Sample Primary Sample 2/10/14 8:46 Water 2/10/14 8:46 Water In Place In Place Primary Result Primary Result Other SVOCs Other SVOCs 8270C SIM 8270C SIM Diethyl phthalate Dimethyl phthalate 84662 131113 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_021014_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 2/10/14 8:46 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 8151A 8151A 8151A 8151A 8151A 8151A 8151A 8151A Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4,5‐T Silvex 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid Dalapon Dicamba Dichlorprop Dinoseb Page 3 of 9 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 60851345 57117314 1746016 51207319 39001020 3268879 93765 93721 94757 94826 75990 1918009 120365 88857 Result  Value 0.095 0.095 0.095 0.06 0.059 120 120 0.0004 0.0004 0.00067 0.00064 0.068 0.057 0.0001 0.00008 0.0001 0.0001 0.00078 0.0005 0.0012 0.0008 0.00028 0.00018 0.0017 0.0015 0.00093 0.00073 0.0021 0.0021 0.000033 0.000033 0.000062 0.00005 0.0026 0.0014 0.027 0.016 0.000027 0.000027 0.12 0.013 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L 9.5 ug/L 0.017 ug/L 9.5 0.0084 0.12 0.0054 0.0049 0.01 0.0095 0.014 0.0031 0.0049 0.0033 0.0034 0.0048 0.003 0.0046 0.0043 0.018 0.014 0.0051 0.0093 0.0077 0.355 0.324 0.355 0.55 0.16 0.092 0.09 0.11 0.087 0.12 0.11 0.35 0.065 0.32 0.099 0.069 0.045 0.07 0.87 4 0.18 0.16 0.2 0.34 0.86 0.14 0.61 0.42 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 240 240 240 60 59 120000 120000 2 2 0.67 0.64 68 57 0.5 0.5 1 1 2 2 2 2 0.28 1 1.7 1.5 2 2 2.1 2.1 1 1 1 1 2.6 1.4 27 16 0.2 0.2 9.5 9.5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N Y Y Y Y N N Y Y Y Y N N N N N N N N Y N Y Y N N Y Y N N N N Y Y Y Y N N N N 9.5 ug/L 9.5 ug/L N N 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 0.000000355 0.000000324 0.000000355 0.000047 0.000047 0.000047 0.000047 0.000047 0.000047 0.000047 0.000047 0.00000035 0.000047 0.00000032 0.000047 0.000047 0.0000095 0.0000095 0.000095 0.000095 0.94 0.94 3.8 3.8 1.9 1.9 3.8 0.94 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N Y Y Y N N N N N N N N Y N Y N N N N N N N N N N N N N N Validation Note U U U U U J J U U U U U U U U J U J J U U J J U U U U J J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U J U J U U U U U U UJ U U U UJ U U U TR TR F F F F TR TR TR F F TR TR BF TR TR TR B; Value changed from 0.43 to  9.5U B; Value changed from 0.017  to 9.5U BF TR TR BF BF C C Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 100 Yes 2.40E+00 ug/L 5 Yes 4.80E+01 ug/L 100 Yes 2.40E+00 ug/L 25 Yes 2.40E+00 ug/L ‐‐ No SL No SL ug/L 190000 No 6.32E‐01 ug/L 190000 No 6.32E‐01 ug/L 2.5 No 8.00E‐01 ug/L 2.5 No 8.00E‐01 ug/L 7.7 No 8.70E‐02 ug/L ug/L 7.7 No 8.31E‐02 150 No 4.53E‐01 ug/L 150 No 3.80E‐01 ug/L 0.14 Yes 3.57E+00 ug/L 0.14 Yes 3.57E+00 ug/L 0.2 Yes 5.00E+00 ug/L 0.2 Yes 5.00E+00 ug/L 14 No 1.43E‐01 ug/L 14 No 1.43E‐01 ug/L 4.7 No 4.26E‐01 ug/L 4.7 No 4.26E‐01 ug/L 11 No 2.55E‐02 ug/L ug/L 11 No 9.09E‐02 2.2 No 7.73E‐01 ug/L 2.2 No 6.82E‐01 ug/L 17 No 1.18E‐01 ug/L 17 No 1.18E‐01 ug/L 1.6 Yes 1.31E+00 ug/L 1.6 Yes 1.31E+00 ug/L 0.17 Yes 5.88E+00 ug/L 0.17 Yes 5.88E+00 ug/L 0.13 Yes 7.69E+00 ug/L 0.13 Yes 7.69E+00 ug/L 2.6 No 1.00E+00 ug/L ug/L 2.6 No 5.38E‐01 6300 No 4.29E‐03 ug/L 6300 No 2.54E‐03 ug/L 0.063 Yes 3.17E+00 ug/L 0.063 Yes 3.17E+00 ug/L 4 Yes 2.38E+00 ug/L 78 No 1.22E‐01 ug/L RL RL Units 0.24 0.24 0.24 0.05 0.05 1 1 0.002 0.002 0.005 0.005 0.005 0.005 0.0005 0.0005 0.001 0.001 0.002 0.002 0.002 0.002 0.001 0.001 0.01 0.01 0.002 0.002 0.005 0.005 0.001 0.001 0.001 0.001 0.005 0.005 0.02 0.02 0.0002 0.0002 9.5 9.5 mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L MDL 0.095 0.095 0.095 0.0026 0.0026 0.092 0.092 0.0004 0.0004 0.00033 0.00033 0.00029 0.00029 0.00008 0.00008 0.0001 0.0001 0.0005 0.0005 0.00056 0.00056 0.00018 0.00018 0.00014 0.00014 0.0003 0.0003 0.0007 0.0007 0.000033 0.000033 0.00005 0.00005 0.0005 0.0005 0.002 0.002 0.000027 0.000027 0.12 0.013 Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.017 ug/L 0.017 ug/L Y Y 10000 130000 No No 9.50E‐04 7.31E‐05 ug/L ug/L 9.5 ug/L 9.5 ug/L 1300 500 0.01 2.6 50 380 380 3800 ‐‐ 0.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 250 ‐‐ 17 3800 380 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.00003 ‐‐ ‐‐ ‐‐ 130 ‐‐ 130 100 ‐‐ ‐‐ ‐‐ 7 No No Yes Yes No No No No No SL Yes No SL No SL No SL No SL No SL No No No SL No No No No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No No SL No SL No SL No No SL No No No SL No SL No SL No 7.31E‐03 1.90E‐02 9.50E+02 3.65E+00 1.90E‐01 2.50E‐02 2.50E‐02 2.50E‐03 No SL 4.75E+01 No SL No SL No SL No SL No SL 3.80E‐02 3.80E‐02 No SL 5.59E‐01 2.50E‐03 2.50E‐02 No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL No SL 3.17E‐01 No SL No SL No SL 7.23E‐03 No SL 2.92E‐02 3.80E‐02 No SL No SL No SL 1.34E‐01 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.01 0.0084 0.12 0.0054 0.0049 0.01 0.0095 0.014 0.0031 0.0049 0.0033 0.0034 0.0048 0.003 0.0046 0.0043 0.018 0.014 0.0051 0.0093 0.0077 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 47 47 47 47 47 47 47 47 47 47 47 47 47 9.5 9.5 95 95 0.94 0.94 3.8 3.8 1.9 1.9 3.8 0.94 pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.076 0.16 0.092 0.09 0.11 0.087 0.12 0.11 0.11 0.065 0.062 0.099 0.069 0.045 0.07 0.042 0.057 0.18 0.16 0.2 0.34 0.86 0.14 0.61 0.42 pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name Sample ID Sample Type Collection Date Matrix  Type Sample Top  Depth (feet bgs) Sample  Bottom  Depth (feet bgs) Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Herbicides Herbicides Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 8151A 8151A 8015B 8015B 8015B 8015B 8015B 8015B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7196A 7470A 7470A MCPA MCPP Diesel Range Organics (C12‐C14) Diesel Range Organics (C15‐C20) Diesel Range Organics (C21‐C30) Gasoline Range Organics (C8‐C11) Diesel Range Organics (C8‐C30) Oil Range Organics (C30‐C40) Sodium Sodium, Dissolved Antimony Antimony, Dissolved Arsenic Arsenic, Dissolved Barium Barium, Dissolved Beryllium Beryllium, Dissolved Cadmium Cadmium, Dissolved Manganese Manganese, Dissolved Silver Silver, Dissolved Hexavalent Chromium Mercury Mercury, Dissolved 94746 93652 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) EFHD (C8‐C11) EFHD (C8‐C30) ORO C30‐C40 7440235 7440235‐D 7440360 7440360‐D 7440382 7440382‐D 7440393 7440393‐D 7440417 7440417‐D 7440439 7440439‐D 7439965 7439965‐D 7440224 7440224‐D 18540299 7439976 7439976‐D EEL EEL EEL CC 1 EEL CC 1 Groundwater Monitoring Well RS‐37 Groundwater Monitoring Well RS‐37 RS‐37_072414_01A RS‐37_072414_01A Primary Sample Primary Sample 7/24/14 12:22 Water 7/24/14 12:22 Water In Place In Place Primary Result Primary Result Other SVOCs Other SVOCs 8270C SIM 8270C SIM bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate 117817 85687 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Groundwater Monitoring Well RS‐37 Groundwater Monitoring Well RS‐37 Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_072414_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 7/24/14 12:22 Water 7/24/14 12:22 Water 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 7/24/14 12:22 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Xylenes, Total 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichloroethane Acetone Benzene Carbon Tetrachloride Chloroform Page 4 of 9 84662 131113 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 1330207 71556 76131 79005 75343 75354 107062 67641 71432 56235 67663 Result  Value 16 31 0.094 0.094 0.094 0.094 0.094 0.094 110 120 0.0004 0.0004 0.00071 0.00073 0.07 0.072 0.00008 0.00008 0.0001 0.0001 0.0064 0.0011 0.000033 0.000033 0.005 0.000027 0.000027 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 9.5 ug/L 0.013 ug/L 9.5 ug/L 0.017 ug/L 9.5 0.0084 0.12 0.0054 0.0049 0.01 0.0094 0.013 0.003 0.0049 0.0033 0.0034 0.0048 0.003 0.0046 0.0043 0.018 0.014 0.005 0.0092 0.0076 0.12 0.2 0.16 0.099 0.087 0.11 0.15 0.0036 0.0036 0.007 0.0028 0.0025 0.0042 0.066 0.0027 0.003 0.0026 0.0027 0.0033 0.0038 0.0042 0.0033 0.0032 0.0036 0.0036 0.0013 0.0061 0.17 0.34 0.16 0.42 0.27 0.22 0.23 0.13 1.9 0.16 0.19 0.16 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 470 470 240 240 240 240 240 470 110000 120000 2 2 0.71 0.73 70 72 0.5 0.5 1 1 6.4 1.1 1 1 20 0.2 0.2 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N Y Y N N Y Y Y Y N N N N Y Y N N N N N J U U U U U 9.5 ug/L 9.5 ug/L N N UJ U 9.5 ug/L 9.5 ug/L 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 0.95 0.95 0.95 0.95 0.95 0.95 0.95 0.0095 0.0095 0.0095 0.0059 0.0059 0.0059 0.059 0.0059 0.0095 0.0095 0.0059 0.0095 0.0095 0.0095 0.0095 0.0059 0.0059 0.0059 0.012 0.047 0.47 2 1 5 1 1 1 0.5 10 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Validation Note U U U U U U U U U U J J TR TR U U U U U U U UJ U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U TR FC;value changed from 0.23 to  9.5U BF;value changed from 0.42 to  9.5U BF;value changed from 0.023  to 9.5U C Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 6.3 Yes 7.46E+01 ug/L 13 Yes 3.62E+01 ug/L 100 Yes 2.40E+00 ug/L 100 Yes 2.40E+00 ug/L 100 Yes 2.40E+00 ug/L 5 Yes 4.80E+01 ug/L 100 Yes 2.40E+00 ug/L 740 No 6.35E‐01 ug/L 190000 No 5.79E‐01 ug/L 190000 No 6.32E‐01 ug/L 2.5 No 8.00E‐01 ug/L 2.5 No 8.00E‐01 ug/L 7.7 No 9.22E‐02 ug/L 7.7 No 9.48E‐02 ug/L 150 No 4.67E‐01 ug/L 150 No 4.80E‐01 ug/L 0.14 Yes 3.57E+00 ug/L 0.14 Yes 3.57E+00 ug/L 0.2 Yes 5.00E+00 ug/L 0.2 Yes 5.00E+00 ug/L 150 No 4.27E‐02 ug/L 150 No 7.33E‐03 ug/L 0.17 Yes 5.88E+00 ug/L 0.17 Yes 5.88E+00 ug/L 14 Yes 1.43E+00 ug/L 0.063 Yes 3.17E+00 ug/L 0.063 Yes 3.17E+00 ug/L RL RL Units 470 470 0.24 0.24 0.24 0.24 0.24 0.47 1 1 0.002 0.002 0.005 0.005 0.005 0.005 0.0005 0.0005 0.001 0.001 0.005 0.005 0.001 0.001 0.02 0.0002 0.0002 ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L MDL 16 31 0.094 0.094 0.094 0.094 0.094 0.094 0.092 0.092 0.0004 0.0004 0.00033 0.00033 0.00029 0.00029 0.00008 0.00008 0.0001 0.0001 0.00031 0.00031 0.000033 0.000033 0.005 0.000027 0.000027 Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 4 78 Yes No 2.38E+00 1.22E‐01 ug/L ug/L 9.5 ug/L 9.5 ug/L 0.12 ug/L 0.013 ug/L 10000 130000 No No 9.50E‐04 7.31E‐05 ug/L ug/L 9.5 ug/L 9.5 ug/L 0.017 ug/L 0.017 ug/L 1300 500 0.01 2.6 50 380 380 3800 ‐‐ 0.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 250 ‐‐ 17 3800 380 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.62 0.44 0.44 0.002 0.015 0.025 0.1 0.084 0.002 75 75 75 2 3.8 3.8 0.2 0.01 0.01 0.0082 30 3 1750 200 1200 5 5 6 0.5 20000 1 0.5 80 No No Yes Yes No No No No No SL Yes No SL No SL No SL No SL No SL No No No SL No No No Yes Yes Yes Yes Yes Yes Yes No No No Yes No No No No Yes No No No No No No No No No Yes No No No No No No No No No No No Yes No 7.31E‐03 1.90E‐02 9.50E+02 3.65E+00 1.90E‐01 2.50E‐02 2.50E‐02 2.50E‐03 No SL 4.75E+01 No SL No SL No SL No SL No SL 3.80E‐02 3.80E‐02 No SL 5.59E‐01 2.50E‐03 2.50E‐02 1.90E+00 1.90E+00 1.90E+00 1.90E+00 1.90E+00 1.90E+00 1.90E+00 1.53E‐02 2.16E‐02 2.16E‐02 2.95E+00 3.93E‐01 2.36E‐01 5.90E‐01 7.02E‐02 4.75E+00 1.27E‐04 7.87E‐05 1.27E‐04 4.75E‐03 2.50E‐03 2.50E‐03 2.95E‐02 5.90E‐01 5.90E‐01 1.46E+00 1.57E‐03 1.57E‐01 1.14E‐03 5.00E‐03 4.17E‐03 2.00E‐01 2.00E‐01 1.67E‐01 1.00E+00 5.00E‐04 1.00E+00 2.00E+00 1.25E‐02 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 9.5 0.95 0.95 0.95 0.95 0.95 0.95 0.95 0.0095 0.0095 0.0095 0.0059 0.0059 0.0059 0.059 0.0059 0.0095 0.0095 0.0059 0.0095 0.0095 0.0095 0.0095 0.0059 0.0059 0.0059 0.012 0.047 0.47 2 1 5 1 1 1 0.5 10 1 1 1 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.01 0.0084 0.12 0.0054 0.0049 0.01 0.0094 0.013 0.003 0.0049 0.0033 0.0034 0.0048 0.003 0.0046 0.0043 0.018 0.014 0.005 0.0092 0.0076 0.12 0.2 0.16 0.099 0.087 0.11 0.15 0.0036 0.0036 0.007 0.0028 0.0025 0.0042 0.066 0.0027 0.003 0.0026 0.0027 0.0033 0.0038 0.0042 0.0033 0.0032 0.0036 0.0036 0.0013 0.0061 0.17 0.34 0.16 0.42 0.27 0.22 0.23 0.13 1.9 0.16 0.19 0.16 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Groundwater Monitoring Well Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 RS‐37 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A RS‐37_101314_01A PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF081 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PF276 Sample ID PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 Sample Type Collection Date Matrix  Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 10/13/14 11:44 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 5/14/01 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Sample Top  Depth (feet bgs) Sample  Bottom  Depth (feet bgs) Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs VOCs Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B 8260B Analyte cis‐1,2‐Dichloroethene Ethylbenzene Methyl ethyl ketone Methylene chloride m‐Xylene & p‐Xylene o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene Trichloroethene Trichlorofluoromethane Vinyl chloride 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloroethenes 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene Methyl ethyl ketone Acetone Benzene Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane cis‐1,2‐Dichloroethene Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Tetrachloroethene Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2,3‐Trichloropropane 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloroethenes 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,4‐Dichlorobenzene Methyl ethyl ketone 2‐Chloroethylvinyl ether 2‐Hexanone Methyl isobutyl ketone (MIBK) Acetone Benzene Bromodichloromethane Bromoform Bromomethane Carbon Disulfide Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Dibromochloromethane Dichlorodifluoromethane Ethylbenzene m‐Xylene & p‐Xylene Methylene chloride o‐Xylene Styrene Tetrachloroethene Page 5 of 9 CAS Number 156592 100414 78933 75092 179601231 95476 127184 108883 156605 79016 75694 75014 630206 71556 79345 79005 75343 75354 95636 96128 95501 107062 540590 108678 541731 106467 78933 67641 71432 75274 75252 74839 56235 108907 75003 67663 74873 156592 75718 100414 179601231 75092 95476 127184 108883 156605 10061026 79016 75694 75014 1330207 630206 71556 79345 79005 76131 75343 75354 96184 95636 96128 95501 107062 540590 78875 108678 541731 106467 78933 110758 591786 108101 67641 71432 75274 75252 74839 75150 56235 108907 75003 67663 74873 79389 156592 10061015 124481 75718 100414 179601231 75092 95476 100425 127184 Result  Value 0.15 0.16 2 0.32 0.34 0.19 0.2 0.17 0.15 0.94 0.29 0.1 5 5 5 5 5 5 5 5 5 5 10 5 5 5 3 5 5 5 5 5 5 5 5 5 5 5 5 5 5 1 5 5 5 5 5 1 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 50 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 1 1 10 5 2 1 1 1 1 0.94 1 1 5 5 5 5 5 5 5 5 5 5 10 5 5 5 3 5 5 5 5 5 5 5 5 5 5 5 5 5 5 1 5 5 5 5 5 1 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 50 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N Y N N N N N N N N N N N N N N N N Y N N N N N N N N N N N N N N Y N N N N N Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U U U U U U U U U J U U U U U U U U U U U U U U U U JB U U U U U U U U U U U U U U J U U U U U J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note TR Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 6 No 1.67E‐01 ug/L 300 No 3.33E‐03 ug/L 3800 No 2.63E‐03 ug/L 5 No 1.00E+00 ug/L 1750 No 1.14E‐03 ug/L 1750 No 5.71E‐04 ug/L 5 No 2.00E‐01 ug/L 150 No 6.67E‐03 ug/L 10 No 1.00E‐01 ug/L 5 No 1.88E‐01 ug/L 150 No 6.67E‐03 ug/L 0.5 Yes 2.00E+00 ug/L ‐‐ No SL No SL ug/L 200 No 2.50E‐02 ug/L 1 Yes 5.00E+00 ug/L 5 No 1.00E+00 ug/L 5 No 1.00E+00 ug/L 6 No 8.33E‐01 ug/L 330 No 1.52E‐02 ug/L 0.2 Yes 2.50E+01 ug/L 600 No 8.33E‐03 ug/L 0.5 Yes 1.00E+01 ug/L ug/L 130 No 7.69E‐02 330 No 1.52E‐02 ug/L 600 No 8.33E‐03 ug/L 5 No 1.00E+00 ug/L 3800 No 7.89E‐04 ug/L 20000 No 2.50E‐04 ug/L 1 Yes 5.00E+00 ug/L 80 No 6.25E‐02 ug/L 80 No 6.25E‐02 ug/L 8.8 No 5.68E‐01 ug/L 0.5 Yes 1.00E+01 ug/L 70 No 7.14E‐02 ug/L 16 No 3.13E‐01 ug/L 80 No 6.25E‐02 ug/L 5.7 No 8.77E‐01 ug/L 6 No 8.33E‐01 ug/L 1000 No 5.00E‐03 ug/L 300 No 1.67E‐02 ug/L 1750 No 2.86E‐03 ug/L 5 No 2.00E‐01 ug/L 1750 No 2.86E‐03 ug/L 5 No 1.00E+00 ug/L 150 No 3.33E‐02 ug/L 10 No 5.00E‐01 ug/L 0.81 Yes 6.17E+00 ug/L 5 No 2.00E‐01 ug/L 150 No 3.33E‐02 ug/L 0.5 Yes 1.00E+01 ug/L ug/L 1750 No 5.71E‐03 ‐‐ No SL No SL ug/L 200 No 2.50E‐02 ug/L 1 Yes 5.00E+00 ug/L 5 No 1.00E+00 ug/L 1200 No 4.17E‐03 ug/L 5 No 1.00E+00 ug/L 6 No 8.33E‐01 ug/L 0.005 Yes 1.00E+03 ug/L 330 No 1.52E‐02 ug/L 0.2 Yes 2.50E+01 ug/L 600 No 8.33E‐03 ug/L 0.5 Yes 1.00E+01 ug/L 130 No 3.85E‐02 ug/L 5 No 1.00E+00 ug/L 330 No 1.52E‐02 ug/L 600 No 8.33E‐03 ug/L 5 No 1.00E+00 ug/L 3800 No 1.32E‐03 ug/L ‐‐ No SL No SL ug/L 250 No 2.00E‐02 ug/L 120 No 4.17E‐02 ug/L 20000 No 2.50E‐04 ug/L 1 Yes 5.00E+00 ug/L 80 No 6.25E‐02 ug/L 80 No 6.25E‐02 ug/L 8.8 No 5.68E‐01 ug/L 160 No 3.13E‐02 ug/L 0.5 Yes 1.00E+01 ug/L 70 No 7.14E‐02 ug/L 16 No 3.13E‐01 ug/L 80 No 6.25E‐02 ug/L 5.7 No 8.77E‐01 ug/L ‐‐ No SL No SL ug/L 6 No 8.33E‐01 ug/L 0.5 Yes 1.00E+01 ug/L 80 No 6.25E‐02 ug/L 1000 No 5.00E‐03 ug/L 300 No 1.67E‐02 ug/L 1750 No 2.86E‐03 ug/L 5 No 1.00E+00 ug/L 1750 No 2.86E‐03 ug/L 100 No 5.00E‐02 ug/L 5 No 1.00E+00 ug/L RL RL Units Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA MDL 1 1 10 5 2 1 1 1 1 1 1 1 5 5 5 5 5 5 5 5 5 5 10 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.15 0.16 2 0.32 0.34 0.19 0.2 0.17 0.15 0.16 0.29 0.1 5 5 5 5 5 5 5 5 5 5 10 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 50 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 5 5 10 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 50 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PF276 PF276 PF276 PF276 PF276 PF276 PF276 PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_DISS_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021009_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L Sample ID PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 PZ050GW01S01 Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 6/3/03 0:00 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/10/09 12:40 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 Matrix  Type Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Sample Top  Depth (feet bgs) Sample  Bottom  Depth (feet bgs) Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class VOCs VOCs VOCs VOCs VOCs VOCs VOCs Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Energetics Energetics Energetics Energetics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Energetics Energetics Energetics Analysis  Method 8260B 8260B 8260B 8260B 8260B 8260B 8260B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7470A 8270C 8270C 8270C 8270C 8015B 8015B 8015B 8015B 8015B 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte Toluene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total Aluminum, Dissolved Barium, Dissolved Boron, Dissolved Cobalt, Dissolved Iron, Dissolved Magnesium, Dissolved Manganese, Dissolved Molybdenum, Dissolved Strontium, Dissolved Tin, Dissolved Vanadium, Dissolved Zinc, Dissolved Antimony, Dissolved Arsenic, Dissolved Beryllium, Dissolved Cadmium, Dissolved Chromium, Dissolved Copper, Dissolved Lead, Dissolved Nickel, Dissolved Selenium, Dissolved Silver, Dissolved Thallium, Dissolved Mercury, Dissolved 1,3‐Dinitrobenzene 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene Diesel Range Organics (C12‐C14) Diesel Range Organics (C15‐C20) Diesel Range Organics (C21‐C30) Gasoline Range Organics (C8‐C11) Diesel Range Organics (C8‐C30) 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitrophenol 3,3'‐Dichlorobenzidine 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Benzidine bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Isophorone n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine p‐Chloro‐m‐cresol Pentachlorophenol Phenol Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene 1,3‐Dinitrobenzene 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Page 6 of 9 CAS Number 108883 156605 10061026 79016 75694 75014 1330207 7429905‐D 7440393‐D 7440428‐D 7440484‐D 7439896‐D 7439954‐D 7439965‐D 7439987‐D 7440246‐D 7440315‐D 7440622‐D 7440666‐D 7440360‐D 7440382‐D 7440417‐D 7440439‐D 7440473‐D 7440508‐D 7439921‐D 7440020‐D 7782492‐D 7440224‐D 7440280‐D 7439976‐D 99650 121142 606202 98953 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) EFHD (C8‐C11) EFHD (C8‐C30) 120821 122667 88062 120832 105679 51285 91587 95578 88755 91941 534521 101553 7005723 100027 92875 111911 111444 108601 117817 85687 84662 131113 84742 117840 118741 87683 67721 78591 62759 621647 86306 59507 87865 108952 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 99650 121142 606202 Result  Value Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code 5 5 5 8 5 5 5 0.0802 0.0935 0.122 0.0021 0.0522 16.6 0.0509 0.0049 0.829 0.0088 0.0042 0.0081 0.0003 0.00095 0.00013 0.00022 0.00068 ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 0.00076 0.00007 0.0012 0.00099 0.00008 0.00015 0.000056 2 1 1 1 0.099 0.099 0.099 0.099 0.099 1 1 1 1 3 20 2 1 1 2 5 1 2 10 20 1 1 1 2 2 2 2 2 2 1 1 1 1 2 1 2 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1 mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 5 5 5 8 5 5 5 200 93.5 122 5 200 16600 50.9 10 829 20 4.2 20 1 2 0.5 0.22 2 2 0.07 1.2 2 0.5 0.5 0.2 5 5 5 5 590 590 590 590 590 5 5 5 5 10 60 5 5 5 5 15 5 5 30 60 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 15 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N Y N N N N Y Y N N Y Y N Y N Y N N N N Y N N Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Validation Note U U U U U U U U U U U J U U U U J U U J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Reported result is less than 5X  or 10X than the associated  field blank. Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 150 No 3.33E‐02 ug/L 10 No 5.00E‐01 ug/L 0.81 Yes 6.17E+00 ug/L 5 Yes 1.60E+00 ug/L 150 No 3.33E‐02 ug/L 0.5 Yes 1.00E+01 ug/L 1750 No 2.86E‐03 ug/L 13000 No 1.54E‐02 ug/L 150 No 6.23E‐01 ug/L 340 No 3.59E‐01 ug/L 1.9 Yes 2.63E+00 ug/L 4100 No 4.88E‐02 ug/L 77000 No 2.16E‐01 ug/L 150 No 3.39E‐01 ug/L 2.2 Yes 4.55E+00 ug/L 800 Yes 1.04E+00 ug/L 2.4 Yes 8.33E+00 ug/L 2.6 Yes 1.62E+00 ug/L 6300 No 3.17E‐03 ug/L 2.5 No 4.00E‐01 ug/L 7.7 No 2.60E‐01 ug/L 0.14 Yes 3.57E+00 ug/L 0.2 Yes 1.10E+00 ug/L 14 No 1.43E‐01 ug/L 4.7 11 17 1.6 0.17 0.13 0.063 1.3 ‐‐ 0.22 110 100 100 100 5 100 5 ‐‐ 2.1 ‐‐ 100 ‐‐ ‐‐ 63 ‐‐ 0.12 1.3 ‐‐ ‐‐ ‐‐ 0.0003 38 360 ‐‐ 4 78 10000 130000 1300 500 1 ‐‐ 10 5400 0.01 0.01 16 ‐‐ 1 4200 380 380 3800 ‐‐ 0.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 250 ‐‐ 17 3800 1.3 ‐‐ 0.22 No No No Yes Yes Yes Yes Yes No SL Yes No Yes Yes Yes Yes Yes No No SL Yes No SL No No SL No SL No No SL Yes Yes No SL No SL No SL Yes No No No SL Yes No No No No No Yes No SL No No Yes Yes No No SL Yes No No No No No SL Yes No SL No SL No SL No SL No SL No No No SL No No Yes No SL Yes 4.26E‐01 6.36E‐03 7.06E‐02 1.25E+00 2.94E+00 3.85E+00 3.17E+00 3.85E+00 No SL 2.27E+01 4.55E‐02 5.90E+00 5.90E+00 5.90E+00 1.18E+02 5.90E+00 1.00E+00 No SL 2.38E+00 No SL 1.00E‐01 No SL No SL 7.94E‐02 No SL 4.17E+01 1.15E+01 No SL No SL No SL 2.00E+05 1.32E‐01 1.39E‐02 No SL 1.25E+00 6.41E‐02 5.00E‐04 3.85E‐05 3.85E‐03 1.00E‐02 5.00E+00 No SL 5.00E‐01 9.26E‐04 5.00E+02 5.00E+02 3.13E‐01 No SL 1.50E+01 1.19E‐03 1.32E‐02 1.32E‐02 1.32E‐03 No SL 2.50E+01 No SL No SL No SL No SL No SL 2.00E‐02 2.00E‐02 No SL 2.94E‐01 1.32E‐03 3.85E+00 No SL 2.27E+01 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL RL Units Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA MDL 5 5 5 5 5 5 5 0.2 0.005 0.05 0.005 0.2 0.1 0.005 0.01 0.005 0.02 0.005 0.02 0.001 0.002 0.0005 0.0005 0.002 ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 5 ug/L 5 ug/L 5 ug/L 5 5 5 0.0802 0.0006 0.0094 0.0021 0.0522 0.0135 0.00084 0.0049 0.00089 0.0088 0.0025 0.0081 0.0003 0.00095 0.00013 0.00021 0.00068 ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 0.002 0.001 0.002 0.002 0.0005 0.0005 0.0002 5 5 5 5 0.59 0.59 0.59 0.59 0.59 5 5 5 5 10 60 5 5 5 5 15 5 5 30 60 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 15 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 0.00038 0.00005 0.0005 0.00099 0.00008 0.00015 0.000056 2 1 1 1 0.099 0.099 0.099 0.099 0.099 1 1 1 1 3 20 2 1 1 2 5 1 2 10 20 1 1 1 2 2 2 2 2 2 1 1 1 1 2 1 2 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1 mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_021908_01_L PZ‐050_042814_01 PZ‐050_042814_01 PZ‐050_042814_01 PZ‐050_042814_01 PZ‐050_042814_01 PZ‐050_042814_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 Sample ID Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 2/19/08 12:09 4/28/14 13:02 4/28/14 13:02 4/28/14 13:02 4/28/14 13:02 4/28/14 13:02 4/28/14 13:02 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 Matrix  Type Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Sample Top  Depth (feet bgs) 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Sample  Bottom  Depth (feet bgs) 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Calculated Result Calculated Result Calculated Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Energetics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Analysis  Method 8270C 8015B 8015B 8015B 8015B 8015B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7470A 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8015B 8015B 8015B 8015B 8015B 8015B 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 Analyte Nitrobenzene Diesel Range Organics (C12‐C14) Diesel Range Organics (C15‐C20) Diesel Range Organics (C21‐C30) Gasoline Range Organics (C8‐C11) Total Petroleum Hydrocarbons Aluminum, Dissolved Barium, Dissolved Boron, Dissolved Cobalt, Dissolved Iron, Dissolved Magnesium, Dissolved Manganese, Dissolved Molybdenum, Dissolved Strontium, Dissolved Tin, Dissolved Vanadium, Dissolved Zinc, Dissolved Antimony, Dissolved Arsenic, Dissolved Beryllium, Dissolved Cadmium, Dissolved Chromium, Dissolved Copper, Dissolved Lead, Dissolved Nickel, Dissolved Selenium, Dissolved Silver, Dissolved Thallium, Dissolved Mercury, Dissolved 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitrophenol 3,3'‐Dichlorobenzidine 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Benzidine bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Isophorone n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine p‐Chloro‐m‐cresol Pentachlorophenol Phenol Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Diesel Range Organics (C12‐C14) Diesel Range Organics (C15‐C20) Diesel Range Organics (C21‐C30) Gasoline Range Organics (C8‐C11) Diesel Range Organics (C8‐C30) Oil Range Organics (C30‐C40) DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Mammal 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin Page 7 of 9 CAS Number 98953 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) EFHD (C8‐C11) TPH 7429905‐D 7440393‐D 7440428‐D 7440484‐D 7439896‐D 7439954‐D 7439965‐D 7439987‐D 7440246‐D 7440315‐D 7440622‐D 7440666‐D 7440360‐D 7440382‐D 7440417‐D 7440439‐D 7440473‐D 7440508‐D 7439921‐D 7440020‐D 7782492‐D 7440224‐D 7440280‐D 7439976‐D 120821 122667 88062 120832 105679 51285 91587 95578 88755 91941 534521 101553 7005723 100027 92875 111911 111444 108601 117817 85687 84662 131113 84742 117840 118741 87683 67721 78591 621647 86306 59507 87865 108952 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) EFHD (C8‐C11) EFHD (C8‐C30) ORO C30‐C40 1746016‐TEQ_Bird 1746016‐TEQ_Fish 1746016‐TEQ_Mammal 67562394 35822469 55673897 70648269 39227286 57117449 57653857 Result  Value 1 0.2 0.2 0.2 0.2 0.2 0.0802 0.0774 0.121 0.0021 0.0522 16.2 0.0572 0.0046 0.773 0.0084 0.0015 0.0315 0.0003 0.0016 0.000052 0.000099 0.0006 0.0094 0.00019 0.0015 0.0029 0.000037 0.000037 0.000056 1 1 1 1 3 20 2 1 1 2 5 1 2 10 20 1 1 1 2 2 2 2 2 2 1 1 1 1 1 2 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0.1 0.1 0.28 0.1 0.29 0.39 0.0032 0.0032 0.0096 0.88 3 0.084 0.051 0.047 0.05 0.051 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L 5 600 600 600 600 600 200 77.4 121 5 200 16200 57.2 10 773 20 5 31.5 1 1.6 0.2 0.25 2 9.4 0.19 1.5 2.9 0.5 0.5 0.2 5 5 5 5 10 59 5 5 5 5 15 5 5 30 59 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 15 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 260 260 280 260 290 390 3.2E‐09 3.2E‐09 9.6E‐09 0.000052 0.000052 0.000052 0.000052 0.000052 0.000052 0.000052 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N Y Y N N Y Y N Y N N Y N Y N N N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y N Y Y Y Y Y N N N N N N N Validation Note U U U U U U U U U U U U U J U U U J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U UJ L U U U U U U U B B Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 110 No 4.55E‐02 ug/L 100 Yes 6.00E+00 ug/L 100 Yes 6.00E+00 ug/L 100 Yes 6.00E+00 ug/L 5 Yes 1.20E+02 ug/L ‐‐ No SL No SL ug/L 13000 No 1.54E‐02 ug/L 150 No 5.16E‐01 ug/L 340 No 3.56E‐01 ug/L 1.9 Yes 2.63E+00 ug/L 4100 No 4.88E‐02 ug/L 77000 No 2.10E‐01 ug/L 150 No 3.81E‐01 ug/L 2.2 Yes 4.55E+00 ug/L 800 No 9.66E‐01 ug/L 2.4 Yes 8.33E+00 ug/L 2.6 Yes 1.92E+00 ug/L 6300 No 5.00E‐03 ug/L 2.5 No 4.00E‐01 ug/L 7.7 No 2.08E‐01 ug/L 0.14 Yes 1.43E+00 ug/L 0.2 Yes 1.25E+00 ug/L 14 No 1.43E‐01 ug/L 4.7 Yes 2.00E+00 ug/L 11 No 1.73E‐02 ug/L ug/L 17 No 8.82E‐02 1.6 Yes 1.81E+00 ug/L 0.17 Yes 2.94E+00 ug/L 0.13 Yes 3.85E+00 ug/L 0.063 Yes 3.17E+00 ug/L 5 No 1.00E+00 ug/L ‐‐ No SL No SL ug/L 2.1 Yes 2.38E+00 ug/L ‐‐ No SL No SL ug/L 100 No 1.00E‐01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 63 No 7.94E‐02 ug/L ‐‐ No SL No SL ug/L 0.12 Yes 4.17E+01 ug/L 1.3 Yes 1.15E+01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 0.0003 Yes 1.97E+05 ug/L 38 No 1.32E‐01 ug/L 360 No 1.39E‐02 ug/L ‐‐ No SL No SL ug/L 4 Yes 1.25E+00 ug/L 78 No 6.41E‐02 ug/L 10000 No 5.00E‐04 ug/L 130000 No 3.85E‐05 ug/L 1300 No 3.85E‐03 ug/L 500 No 1.00E‐02 ug/L 1 Yes 5.00E+00 ug/L ‐‐ No SL No SL ug/L 10 No 5.00E‐01 ug/L 5400 No 9.26E‐04 ug/L 0.01 Yes 5.00E+02 ug/L 16 No 3.13E‐01 ug/L ‐‐ No SL No SL ug/L 1 Yes 1.50E+01 ug/L 4200 No 1.19E‐03 ug/L ug/L 380 No 1.32E‐02 380 No 1.32E‐02 ug/L 3800 No 1.32E‐03 ug/L ‐‐ No SL No SL ug/L 0.2 Yes 2.50E+01 ug/L ug/L ‐‐ No SL No SL ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 250 No 2.00E‐02 ug/L 250 No 2.00E‐02 ug/L ‐‐ No SL No SL ug/L 17 No 2.94E‐01 ug/L 3800 No 1.32E‐03 ug/L 100 Yes 2.60E+00 ug/L 100 Yes 2.60E+00 ug/L 100 Yes 2.80E+00 ug/L 5 Yes 5.20E+01 ug/L 100 Yes 2.90E+00 ug/L 740 No 5.27E‐01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L No SL ug/L ‐‐ No SL ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L RL RL Units MDL Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA 5 0.6 0.6 0.6 0.6 0.6 0.2 0.005 0.05 0.005 0.2 0.1 0.005 0.01 0.005 0.02 0.005 0.02 0.001 0.002 0.0002 0.00025 0.002 0.001 0.001 0.002 0.002 0.0005 0.0005 0.0002 5 5 5 5 10 59 5 5 5 5 15 5 5 30 59 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 15 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 0.26 0.26 0.26 0.26 0.26 0.26 ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L 1 0.2 0.2 0.2 0.2 0.2 0.0802 0.0006 0.0094 0.0021 0.0522 0.0135 0.00084 0.0046 0.00085 0.0084 0.0015 0.0081 0.0003 0.0007 0.000052 0.000099 0.0006 0.00038 0.00005 0.0005 0.00053 0.000037 0.000037 0.000056 1 1 1 1 3 20 2 1 1 2 5 1 2 10 20 1 1 1 2 2 2 2 2 2 1 1 1 1 1 2 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0.1 0.1 0.1 0.1 0.1 0.1 ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L 52 52 52 52 52 52 52 pg/L pg/L pg/L pg/L pg/L pg/L pg/L 0.057 0.076 0.084 0.051 0.047 0.05 0.051 pg/L pg/L pg/L pg/L pg/L pg/L pg/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site Cluster Object Type Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name Sample ID Sample Type Collection Date Matrix  Type Sample Top  Depth (feet bgs) EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 EEL EEL EEL CC 1 EEL CC 1 Piezometer Piezometer PZ‐050 PZ‐050_042914_01 PZ‐050 PZ‐050_042914_01 Primary Sample Primary Sample 4/29/14 7:52 Water 4/29/14 7:52 Water 6 6 EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01 PZ‐050_042914_01A PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 7:52 4/29/14 13:23 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 6 Sample  Bottom  Depth (feet bgs) 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 Remediation  Status Result Type Analytical Class Analysis  Method Analyte CAS Number In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Inorganics Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Other SVOCs Other SVOCs 8290 8290 8290 8290 8290 8290 8290 8290 8290 8290 6860 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7470A 7470A 8270C SIM 8270C SIM 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Perchlorate Sodium Sodium, Dissolved Antimony Antimony, Dissolved Arsenic Arsenic, Dissolved Barium Barium, Dissolved Beryllium Beryllium, Dissolved Cadmium Cadmium, Dissolved Manganese Manganese, Dissolved Silver Silver, Dissolved Mercury Mercury, Dissolved bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate 72918219 19408743 57117416 40321764 60851345 57117314 1746016 51207319 39001020 3268879 14797730 7440235 7440235‐D 7440360 7440360‐D 7440382 7440382‐D 7440393 7440393‐D 7440417 7440417‐D 7440439 7440439‐D 7439965 7439965‐D 7440224 7440224‐D 7439976 7439976‐D 117817 85687 16 In Place 16 In Place Primary Result Primary Result Other SVOCs Other SVOCs 8270C SIM 8270C SIM Diethyl phthalate Dimethyl phthalate 84662 131113 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 16 In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PCBs PCBs PCBs PCBs PCBs PCBs PCBs Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8270C SIM 8082 8082 8082 8082 8082 8082 8082 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 8081A 7196A 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B 6010B Di‐n‐butyl phthalate Di‐n‐octyl phthalate n‐Nitrosodimethylamine 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Pyrene Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Aldrin alpha‐BHC beta‐BHC Chlordane delta‐BHC Dieldrin Endosulfan sulfate Endosulfan I Endosulfan II Endrin Endrin aldehyde Endrin ketone gamma‐BHC Heptachlor Heptachlor epoxide Mirex Methoxychlor Toxaphene Hexavalent Chromium Aluminum, Dissolved Barium, Dissolved Boron, Dissolved Cobalt, Dissolved Iron, Dissolved Magnesium, Dissolved Manganese, Dissolved Molybdenum, Dissolved Strontium, Dissolved Page 8 of 9 84742 117840 62759 90120 91576 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 129000 12674112 11104282 11141165 53469219 12672296 11097691 11096825 72548 72559 50293 309002 319846 319857 57749 319868 60571 1031078 959988 33213659 72208 7421934 53494705 58899 76448 1024573 2385855 72435 8001352 18540299 7429905‐D 7440393‐D 7440428‐D 7440484‐D 7439896‐D 7439954‐D 7439965‐D 7439987‐D 7440246‐D Result  Value 0.052 0.046 0.044 0.026 0.042 0.039 0.017 0.024 2.1 32 0.83 89 82 0.0018 0.0015 0.003 0.001 0.14 0.084 0.00014 0.00008 0.0019 0.00086 0.16 0.008 0.000046 0.000033 0.000027 0.000027 0.4 0.061 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L 11 ug/L 0.019 ug/L 11 0.0093 0.14 0.006 0.0054 0.011 0.01 0.015 0.0034 0.0054 0.0036 0.0037 0.0053 0.0034 0.0051 0.0048 0.02 0.015 0.0056 0.01 0.0085 0.13 0.23 0.18 0.11 0.098 0.12 0.17 0.0041 0.0041 0.0081 0.0033 0.0028 0.0048 0.076 0.0032 0.0035 0.0031 0.0032 0.0038 0.0044 0.0048 0.0038 0.0037 0.0041 0.0041 0.0015 0.0071 0.2 0.005 0.217 0.065 0.111 0.0021 0.267 15.3 0.029 0.0046 0.742 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L 0.000052 0.000052 0.000052 0.000052 0.000052 0.000052 0.00001 0.00001 0.0001 0.000032 0.83 89000 82000 2 1.5 3 1 140 84 0.14 0.5 1.9 0.86 160 8 0.046 1 0.2 0.2 0.4 0.061 Validation Note ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N Y Y Y Y N Y Y Y Y Y Y N Y Y Y Y Y N N N Y Y U U U U U U U U U J J B TR Q U J J J B TR TR TR J U TR J TR J U U U J J TR 11 ug/L 11 ug/L N N U U 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 1.1 1.1 1.1 1.1 1.1 1.1 1.1 0.011 0.011 0.011 0.0068 0.0068 0.0068 0.068 0.0068 0.011 0.011 0.0068 0.011 0.011 0.011 0.011 0.0068 0.0068 0.0068 0.014 0.054 0.54 20 217 65 111 5 267 15300 29 10 742 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N Y Y Y N Y Y Y N Y U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U TR TR B; Value changed from 0.065  to 11U B; Value changed from 0.05 to  11U Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 0.00003 No 3.33E‐01 ug/L ug/L ‐‐ No SL No SL ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 6 No 1.38E‐01 ug/L 190000 No 4.68E‐01 ug/L 190000 No 4.32E‐01 ug/L 2.5 No 8.00E‐01 ug/L 2.5 No 6.00E‐01 ug/L 7.7 No 3.90E‐01 ug/L 7.7 No 1.30E‐01 ug/L 150 No 9.33E‐01 ug/L 150 No 5.60E‐01 ug/L 0.14 No 1.00E+00 ug/L 0.14 Yes 3.57E+00 ug/L 0.2 Yes 9.50E+00 ug/L 0.2 Yes 4.30E+00 ug/L 150 Yes 1.07E+00 ug/L 150 No 5.33E‐02 ug/L 0.17 No 2.71E‐01 ug/L 0.17 Yes 5.88E+00 ug/L 0.063 Yes 3.17E+00 ug/L 0.063 Yes 3.17E+00 ug/L 4 No 1.00E‐01 ug/L 78 No 7.82E‐04 ug/L 10000 130000 No No 1.10E‐03 8.46E‐05 ug/L ug/L 1300 500 0.01 2.6 50 380 380 3800 ‐‐ 0.2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 250 250 ‐‐ 17 3800 380 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.62 0.44 0.44 0.002 0.015 0.025 0.1 0.084 0.002 75 75 75 2 3.8 3.8 0.2 0.01 0.01 0.0082 30 3 14 13000 150 340 1.9 4100 77000 150 2.2 800 No No Yes Yes No No No No No SL Yes No SL No SL No SL No SL No SL No No No SL No No No Yes Yes Yes Yes Yes Yes Yes No No No Yes No No No No Yes No No No No No No No No No Yes No No Yes No No No Yes No No No Yes No 8.46E‐03 2.20E‐02 1.10E+03 4.23E+00 2.20E‐01 2.89E‐02 2.89E‐02 2.89E‐03 No SL 5.50E+01 No SL No SL No SL No SL No SL 4.40E‐02 4.40E‐02 No SL 6.47E‐01 2.89E‐03 2.89E‐02 2.20E+00 2.20E+00 2.20E+00 2.20E+00 2.20E+00 2.20E+00 2.20E+00 1.77E‐02 2.50E‐02 2.50E‐02 3.40E+00 4.53E‐01 2.72E‐01 6.80E‐01 8.10E‐02 5.50E+00 1.47E‐04 9.07E‐05 1.47E‐04 5.50E‐03 2.89E‐03 2.89E‐03 3.40E‐02 6.80E‐01 6.80E‐01 1.71E+00 1.80E‐03 1.80E‐01 1.43E+00 1.67E‐02 4.33E‐01 3.26E‐01 2.63E+00 6.51E‐02 1.99E‐01 1.93E‐01 4.55E+00 9.28E‐01 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L RL RL Units 52 52 52 52 52 52 10 10 100 100 0.05 1 1 0.002 0.002 0.005 0.005 0.005 0.005 0.0005 0.0005 0.001 0.001 0.005 0.005 0.001 0.001 0.0002 0.0002 11 11 pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L 11 ug/L 11 ug/L 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 11 1.1 1.1 1.1 1.1 1.1 1.1 1.1 0.011 0.011 0.011 0.0068 0.0068 0.0068 0.068 0.0068 0.011 0.011 0.0068 0.011 0.011 0.011 0.011 0.0068 0.0068 0.0068 0.014 0.054 0.54 0.02 0.2 0.005 0.05 0.005 0.2 0.1 0.005 0.01 0.005 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L MDL 0.052 0.046 0.044 0.026 0.042 0.039 0.017 0.024 0.042 0.1 0.0088 0.092 0.092 0.0004 0.0004 0.00033 0.00033 0.00029 0.00029 0.00008 0.00008 0.0001 0.0001 0.00031 0.00031 0.000033 0.000033 0.000027 0.000027 0.14 0.014 Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L pg/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y 0.019 ug/L 0.019 ug/L Y Y 0.012 0.0093 0.14 0.006 0.0054 0.011 0.01 0.015 0.0034 0.0054 0.0036 0.0037 0.0053 0.0034 0.0051 0.0048 0.02 0.015 0.0056 0.01 0.0085 0.13 0.23 0.18 0.11 0.098 0.12 0.17 0.0041 0.0041 0.0081 0.0033 0.0028 0.0048 0.076 0.0032 0.0035 0.0031 0.0032 0.0038 0.0044 0.0048 0.0038 0.0037 0.0041 0.0041 0.0015 0.0071 0.2 0.005 0.0802 0.0006 0.0094 0.0021 0.0522 0.0135 0.00084 0.0046 0.00085 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Groundwater APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Groundwater RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object Type Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Piezometer Parent  Object  Sample Name (unique ID or  Sample  Name unique designation) Name PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050 PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_DISS_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L PZ‐050_050708_01_L Sample ID Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 5/7/08 9:45 Matrix  Type Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Water Sample Top  Depth (feet bgs) Sample  Bottom  Depth (feet bgs) Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Energetics Energetics Energetics Energetics Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Hydrocarbons Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs Other SVOCs PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH Analysis  Method 6010B 6010B 6010B 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 6020 7470A 8270C 8270C 8270C 8270C 8015B 8015B 8015B 8015B 8015B 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C 8270C Analyte Tin, Dissolved Vanadium, Dissolved Zinc, Dissolved Antimony, Dissolved Arsenic, Dissolved Beryllium, Dissolved Cadmium, Dissolved Chromium, Dissolved Copper, Dissolved Lead, Dissolved Nickel, Dissolved Selenium, Dissolved Silver, Dissolved Thallium, Dissolved Mercury, Dissolved 1,3‐Dinitrobenzene 2,4‐Dinitrotoluene 2,6‐Dinitrotoluene Nitrobenzene Diesel Range Organics (C12‐C14) Diesel Range Organics (C15‐C20) Diesel Range Organics (C21‐C30) Gasoline Range Organics (C8‐C11) Diesel Range Organics (C8‐C30) 1,2,4‐Trichlorobenzene 1,2‐Diphenylhydrazine 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitrophenol 3,3'‐Dichlorobenzidine 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Benzidine bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Isophorone n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine p‐Chloro‐m‐cresol Pentachlorophenol Phenol Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3‐cd)pyrene Naphthalene Phenanthrene Page 9 of 9 CAS Number 7440315‐D 7440622‐D 7440666‐D 7440360‐D 7440382‐D 7440417‐D 7440439‐D 7440473‐D 7440508‐D 7439921‐D 7440020‐D 7782492‐D 7440224‐D 7440280‐D 7439976‐D 99650 121142 606202 98953 EFHD (C12‐C14) EFHD (C15‐C20) EFHD (C21‐C30) EFHD (C8‐C11) EFHD (C8‐C30) 120821 122667 88062 120832 105679 51285 91587 95578 88755 91941 534521 101553 7005723 100027 92875 111911 111444 108601 117817 85687 84662 131113 84742 117840 118741 87683 67721 78591 621647 86306 59507 87865 108952 83329 208968 120127 56553 50328 205992 191242 207089 218019 53703 206440 86737 193395 91203 85018 Result  Value 0.0084 0.0028 0.0081 0.0003 0.0032 0.000052 0.00014 0.0006 0.0021 0.00018 0.0014 0.0077 0.000037 0.00015 0.000056 2 1 1 1 0.19 0.19 0.19 0.19 0.19 1 1 1 1 3 19 2 1 1 2 5 1 2 10 19 1 1 1 2 2 2 2 2 2 1 1 1 1 1 2 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Result  Project  Result in SL  Value  SL Units Detected Qual  Units Units Code mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L 20 2.8 20 1 3.2 0.2 0.14 2 2.1 0.18 1.4 7.7 0.5 0.5 0.2 5 5 5 5 570 570 570 570 570 5 5 5 5 10 58 5 5 5 5 15 5 5 29 58 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 15 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L N Y N N Y N Y N Y Y Y Y N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N N U J U U U J U J J U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U U Validation Note Boeing  Exceeds  Ratio To  Groundwater  GCL  Boeing  Boeing  Char Level  Groundwater  Groundwater  Units (ug/L) Char Level Char Level 2.4 Yes 8.33E+00 ug/L 2.6 Yes 1.08E+00 ug/L 6300 No 3.17E‐03 ug/L 2.5 No 4.00E‐01 ug/L 7.7 No 4.16E‐01 ug/L 0.14 Yes 1.43E+00 ug/L 0.2 No 7.00E‐01 ug/L 14 No 1.43E‐01 ug/L 4.7 No 4.47E‐01 ug/L 11 No 1.64E‐02 ug/L 17 No 8.24E‐02 ug/L 1.6 Yes 4.81E+00 ug/L 0.17 Yes 2.94E+00 ug/L 0.13 Yes 3.85E+00 ug/L 0.063 Yes 3.17E+00 ug/L 1.3 Yes 3.85E+00 ug/L ‐‐ No SL No SL ug/L 0.22 Yes 2.27E+01 ug/L 110 No 4.55E‐02 ug/L 100 Yes 5.70E+00 ug/L 100 Yes 5.70E+00 ug/L 100 Yes 5.70E+00 ug/L 5 Yes 1.14E+02 ug/L 100 Yes 5.70E+00 ug/L 5 No 1.00E+00 ug/L ‐‐ No SL No SL ug/L 2.1 Yes 2.38E+00 ug/L ‐‐ No SL No SL ug/L 100 No 1.00E‐01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 63 No 7.94E‐02 ug/L ‐‐ No SL No SL ug/L 0.12 Yes 4.17E+01 ug/L 1.3 Yes 1.15E+01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L No SL No SL ug/L ‐‐ 0.0003 Yes 1.93E+05 ug/L 38 No 1.32E‐01 ug/L 360 No 1.39E‐02 ug/L ‐‐ No SL No SL ug/L 4 Yes 1.25E+00 ug/L 78 No 6.41E‐02 ug/L 10000 No 5.00E‐04 ug/L 130000 No 3.85E‐05 ug/L 1300 No 3.85E‐03 ug/L 500 No 1.00E‐02 ug/L 1 Yes 5.00E+00 ug/L ‐‐ No SL No SL ug/L 10 No 5.00E‐01 ug/L 5400 No 9.26E‐04 ug/L 0.01 Yes 5.00E+02 ug/L 16 No 3.13E‐01 ug/L ‐‐ No SL No SL ug/L 1 Yes 1.50E+01 ug/L 4200 No 1.19E‐03 ug/L 380 No 1.32E‐02 ug/L 380 No 1.32E‐02 ug/L 3800 No 1.32E‐03 ug/L ‐‐ No SL No SL ug/L 0.2 Yes 2.50E+01 ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L ‐‐ No SL No SL ug/L 250 No 2.00E‐02 ug/L 250 No 2.00E‐02 ug/L ‐‐ No SL No SL ug/L 17 No 2.94E‐01 ug/L 3800 No 1.32E‐03 ug/L RL 0.02 0.005 0.02 0.001 0.002 0.0002 0.00025 0.002 0.001 0.001 0.002 0.002 0.0005 0.0005 0.0002 5 5 5 5 0.57 0.57 0.57 0.57 0.57 5 5 5 5 10 58 5 5 5 5 15 5 5 29 58 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 15 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 5 RL Units mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L MDL 0.0084 0.0015 0.0081 0.0003 0.0007 0.000052 0.000099 0.0006 0.00038 0.00005 0.0005 0.00099 0.000037 0.00015 0.000056 2 1 1 1 0.19 0.19 0.19 0.19 0.19 1 1 1 1 3 19 2 1 1 2 5 1 2 10 19 1 1 1 2 2 2 2 2 2 1 1 1 1 1 2 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Samples  Samples  Best  MDL  included  included  Pick? Units in ERA in HHRA mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L mg/L mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil-RAD APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil‐RAD RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object  Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐11 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 Sample Name (unique  Parent  Sample  ID or unique  Sample  ID designation) Name SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐011‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Analysis  Method Analyte CAS Number Actinium‐227 Actinium‐228 Americium‐241 Americium‐243 Bismuth‐212 Bismuth‐214 Carbon‐14 Cadmium‐113m Curium‐243/244 Cobalt‐60 Cesium‐134 Cesium‐137 Europium‐152 Europium‐154 Europium‐155 Holmium‐166m Iodine‐129 Potassium‐40 Sodium‐22 Niobium‐94 Nickel‐59 Nickel‐63 Neptunium‐236 Neptunium‐239 Protactinium‐231 Lead‐212 Lead‐214 Promethium‐147 Plutonium‐238 Plutonium‐239/240 Antimony‐125 Antimony‐126 Strontium‐90 Technetium‐99 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Thallium‐208 Thulium‐171 Tritium Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 Actinium‐227 Actinium‐228 Americium‐241 Americium‐243 Bismuth‐212 Bismuth‐214 Carbon‐14 Cadmium‐113m Curium‐243/244 Cobalt‐60 Cesium‐134 Cesium‐137 Europium‐152 Europium‐154 Europium‐155 Holmium‐166m Iodine‐129 Potassium‐40 Sodium‐22 Niobium‐94 Nickel‐59 Nickel‐63 Neptunium‐236 Neptunium‐239 Protactinium‐231 Lead‐212 Lead‐214 Promethium‐147 Plutonium‐238 Plutonium‐239/240 Antimony‐125 Antimony‐126 Strontium‐90 Technetium‐99 Thorium‐228 Thorium‐229 Result  Value Result  Value  Units 14952400 ‐0.00884 pCi/g 14331830 0.993 pCi/g 14596102 0.00548 pCi/g 7440359 0 pCi/g 14913496 0.693 pCi/g 14733030 0.912 pCi/g 14762755 ‐0.157 pCi/g 14336664 ‐46.7 pCi/g 15757876/13981152 0.0128 pCi/g 10198400 0.000121 pCi/g 13967709 0.0109 pCi/g 10045973 0.0366 pCi/g 14683239 0.00389 pCi/g 15585101 ‐0.0656 pCi/g 14391163 0.0687 pCi/g 13967652 ‐0.0102 pCi/g 15046841 0.0039 pCi/g 13966002 18.6 pCi/g 13966320 ‐0.0112 pCi/g 14681631 0.0035 pCi/g E‐16032 ‐0.331 pCi/g E‐16033 ‐0.177 pCi/g 15700364 ‐0.00242 pCi/g 13968597 0.0422 pCi/g 14331852 0.106 pCi/g 15092941 1.2 pCi/g 15067284 1.01 pCi/g 14380757 ‐3.99 pCi/g 13981163 ‐0.00195 pCi/g E‐13207 0 pCi/g 14234356 0.00671 pCi/g 15756328 ‐0.00389 pCi/g 10098972 ‐0.0365 pCi/g 14133767 ‐0.0188 pCi/g 14274829 0.761 pCi/g 15594544 0.00606 pCi/g 14269637 0.599 pCi/g 7440291‐R 0.76 pCi/g 15065108 1.34 pCi/g 14913509 0.364 pCi/g 14333450 0.75 pCi/g 10028178 0.63 pCi/g E‐13230 0.48 pCi/g E‐16045 0.0349 pCi/g 7440611‐R 0.549 pCi/g 10098916 ‐0.0365 pCi/g 14952400 ‐0.0422 pCi/g 14331830 1.08 pCi/g 14596102 0.00543 pCi/g 7440359 0.0129 pCi/g 14913496 0.764 pCi/g 14733030 0.856 pCi/g 14762755 ‐0.155 pCi/g 14336664 ‐33 pCi/g 15757876/13981152 0.00182 pCi/g 10198400 ‐0.00116 pCi/g 13967709 0.00274 pCi/g 10045973 0.0166 pCi/g 14683239 ‐0.0109 pCi/g 15585101 ‐0.0365 pCi/g 14391163 0.0709 pCi/g 13967652 0.00585 pCi/g 15046841 0.0714 pCi/g 13966002 19.2 pCi/g 13966320 ‐0.00841 pCi/g 14681631 0.00167 pCi/g E‐16032 0.0394 pCi/g E‐16033 ‐0.509 pCi/g 15700364 ‐0.00754 pCi/g 13968597 ‐0.00864 pCi/g 14331852 0.103 pCi/g 15092941 1.2 pCi/g 15067284 0.948 pCi/g 14380757 ‐0.46 pCi/g 13981163 0.002 pCi/g E‐13207 0 pCi/g 14234356 0.00905 pCi/g 15756328 0.00187 pCi/g 10098972 0.0292 pCi/g 14133767 0.616 pCi/g 14274829 1.07 pCi/g 15594544 0.0222 pCi/g Page 1 of 3 Result  in SL  Units ‐0.00884 0.993 0.00548 0 0.693 0.912 ‐0.157 ‐46.7 0.0128 0.000121 0.0109 0.0366 0.00389 ‐0.0656 0.0687 ‐0.0102 0.0039 18.6 ‐0.0112 0.0035 ‐0.331 ‐0.177 ‐0.00242 0.0422 0.106 1.2 1.01 ‐3.99 ‐0.00195 0 0.00671 ‐0.00389 ‐0.0365 ‐0.0188 0.761 0.00606 0.599 0.76 1.34 0.364 0.75 0.63 0.48 0.0349 0.549 ‐0.0365 ‐0.0422 1.08 0.00543 0.0129 0.764 0.856 ‐0.155 ‐33 0.00182 ‐0.00116 0.00274 0.0166 ‐0.0109 ‐0.0365 0.0709 0.00585 0.0714 19.2 ‐0.00841 0.00167 0.0394 ‐0.509 ‐0.00754 ‐0.00864 0.103 1.2 0.948 ‐0.46 0.002 0 0.00905 0.00187 0.0292 0.616 1.07 0.0222 SL Detected Units pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g N Y Y N Y Y N N Y N Y Y N N Y N N Y N N N N N N N Y Y N N N N N N N Y N Y Y Y Y N N Y Y Y N N Y Y Y Y Y N N Y N N Y N N Y N N Y N N N N N N N Y Y N N N N N N N Y N Project  Qual  Validation Note Code U U U U U J U UJ J U U UJ U UJ U U U U U U U U U U U U U U U U U U U U U U J U U UJ U UJ U U U U U U U U U U U U Boeing Soil Char Level  (pCi/g) 2.5 679 1.8 ‐‐ 2800 7950 ‐‐ ‐‐ 0.331 0.0389 0.163 0.157 0.0406 0.0479 3.63 ‐‐ 1.134 26 0.0902 0.016 ‐‐ ‐‐ ‐‐ 626 0.562 3550 44800 ‐‐ 2.95 2.58 0.472 ‐‐ 0.24 ‐‐ 23.4 ‐‐ 3.46 3.07 280 23100 ‐‐ 4.892 3.86 0.192 1.52 ‐‐ 2.5 679 1.8 ‐‐ 2800 7950 ‐‐ ‐‐ 0.331 0.0389 0.163 0.157 0.0406 0.0479 3.63 ‐‐ 1.134 26 0.0902 0.016 ‐‐ ‐‐ ‐‐ 626 0.562 3550 44800 ‐‐ 2.95 2.58 0.472 ‐‐ 0.24 ‐‐ 23.4 ‐‐ Exceeds Boeing Soil Char Level No No No No SL No No No SL No SL No No No No No No No No SL No No No No No SL No SL No SL No No No No No SL No No No No SL No No SL No No SL No No No No No SL No No No No No SL No No No No SL No No No SL No SL No No No No No No No No SL No No No No No SL No SL No SL No No No No No SL No No No No SL No No SL No No SL Ratio Boeing Soil Char Level ‐3.54E‐03 1.46E‐03 3.04E‐03 No SL 2.48E‐04 1.15E‐04 No SL No SL 3.87E‐02 3.11E‐03 6.69E‐02 2.33E‐01 9.58E‐02 ‐1.37E+00 1.89E‐02 No SL 3.44E‐03 7.15E‐01 ‐1.24E‐01 2.19E‐01 No SL No SL No SL 6.74E‐05 1.89E‐01 3.38E‐04 2.25E‐05 No SL ‐6.61E‐04 0.00E+00 1.42E‐02 No SL ‐1.52E‐01 No SL 3.25E‐02 No SL 1.73E‐01 2.48E‐01 4.79E‐03 1.58E‐05 No SL 1.29E‐01 1.24E‐01 1.82E‐01 3.61E‐01 No SL ‐1.69E‐02 1.59E‐03 3.02E‐03 No SL 2.73E‐04 1.08E‐04 No SL No SL 5.50E‐03 ‐2.98E‐02 1.68E‐02 1.06E‐01 ‐2.68E‐01 ‐7.62E‐01 1.95E‐02 No SL 6.30E‐02 7.38E‐01 ‐9.32E‐02 1.04E‐01 No SL No SL No SL ‐1.38E‐05 1.83E‐01 3.38E‐04 2.12E‐05 No SL 6.78E‐04 0.00E+00 1.92E‐02 No SL 1.22E‐01 No SL 4.57E‐02 No SL SCL Basis EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG Background EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG SCL Units +/‐ Error +/‐ Error  Units pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g 0.0528 0.043 0.00408 0.00595 0.0591 0.0314 0.196 36 0.00661 0.00407 0.00419 0.00608 0.0138 0.0258 0.0228 0.00643 0.0358 0.801 0.00507 0.00378 0.19 0.223 0.00999 0.0344 0.214 0.0658 0.0378 2.03 0.00338 0.00478 0.0121 0.00424 0.044 0.31 0.0747 0.0264 0.0626 0.0693 0.129 0.0173 3.51 1.57 0.0451 0.0157 0.0461 0.044 0.0467 0.0453 0.00405 0.00517 0.0619 0.0295 0.206 31.7 0.00315 0.00415 0.00413 0.00486 0.0127 0.023 0.0225 0.00663 0.0397 0.822 0.00552 0.00382 0.532 0.266 0.0101 0.0319 0.201 0.0541 0.0314 1.85 0.00447 0.00489 0.0107 0.00422 0.0493 0.406 0.0816 0.0193 MDC 0.176 0.083 0.00495 0.0226 0.101 0.0267 0.667 114 0.017 0.0141 0.0131 0.0138 0.0422 0.0799 0.0553 0.0212 0.128 0.109 0.0166 0.013 0.672 0.752 0.0316 0.116 0.715 0.0283 0.0287 7.3 0.0144 0.0181 0.04 0.0142 0.18 1.05 0.107 0.0962 0.0651 0.056 0.247 0.0136 10 5.48 0.0591 0.0364 0.0338 0.18 0.158 0.0745 0.0049 0.0106 0.11 0.0252 0.699 104 0.00492 0.014 0.0122 0.0138 0.0394 0.0759 0.0602 0.0222 0.191 0.106 0.0161 0.0127 1.87 0.915 0.0329 0.109 0.668 0.0273 0.0281 6.38 0.0147 0.0185 0.0366 0.0141 0.177 1.34 0.0849 0.0599 Samples  Samples  MDC  Best  included in  included in  Units Pick? ERA HHRA pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil-RAD APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil‐RAD RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object  Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐12 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐13 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 Sample Name (unique  Parent  Sample  ID or unique  Sample  ID designation) Name SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 Sample Type Collection Date Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 Matrix  Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Analysis  Method Analyte CAS Number Thorium‐230 Thorium‐232 Thorium‐234 Thallium‐208 Thulium‐171 Tritium Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 Actinium‐227 Actinium‐228 Americium‐241 Americium‐243 Bismuth‐212 Bismuth‐214 Carbon‐14 Cadmium‐113m Curium‐243/244 Cobalt‐60 Cesium‐134 Cesium‐137 Europium‐152 Europium‐154 Europium‐155 Holmium‐166m Iodine‐129 Potassium‐40 Sodium‐22 Niobium‐94 Nickel‐59 Nickel‐63 Neptunium‐236 Neptunium‐239 Protactinium‐231 Lead‐212 Lead‐214 Promethium‐147 Plutonium‐238 Plutonium‐239/240 Antimony‐125 Antimony‐126 Strontium‐90 Technetium‐99 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Thallium‐208 Thulium‐171 Tritium Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 Actinium‐227 Actinium‐228 Americium‐241 Americium‐243 Bismuth‐212 Bismuth‐214 Carbon‐14 Cadmium‐113m Curium‐243/244 Cobalt‐60 Cesium‐134 Cesium‐137 Europium‐152 Europium‐154 Europium‐155 Holmium‐166m Iodine‐129 Potassium‐40 Sodium‐22 Niobium‐94 Nickel‐59 Nickel‐63 Neptunium‐236 Neptunium‐239 Protactinium‐231 Lead‐212 Result  Value Result  Value  Units 14269637 0.666 pCi/g 7440291‐R 1.01 pCi/g 15065108 1.02 pCi/g 14913509 0.37 pCi/g 14333450 ‐6.11 pCi/g 10028178 ‐0.752 pCi/g E‐13230 0.62 pCi/g E‐16045 0.0252 pCi/g 7440611‐R 0.518 pCi/g 10098916 0.0292 pCi/g 14952400 0.0388 pCi/g 14331830 1.07 pCi/g 14596102 0.0135 pCi/g 7440359 ‐0.00232 pCi/g 14913496 0.808 pCi/g 14733030 0.862 pCi/g 14762755 ‐0.288 pCi/g 14336664 32.3 pCi/g 15757876/13981152 0.00582 pCi/g 10198400 ‐0.00177 pCi/g 13967709 ‐0.00148 pCi/g 10045973 0.0373 pCi/g 14683239 ‐0.00953 pCi/g 15585101 ‐0.0277 pCi/g 14391163 0.089 pCi/g 13967652 ‐0.013 pCi/g 15046841 0.0198 pCi/g 13966002 19.6 pCi/g 13966320 ‐0.0031 pCi/g 14681631 0.00435 pCi/g E‐16032 ‐0.288 pCi/g E‐16033 ‐0.354 pCi/g 15700364 ‐0.00514 pCi/g 13968597 0.037 pCi/g 14331852 0.0319 pCi/g 15092941 1.21 pCi/g 15067284 0.956 pCi/g 14380757 0.145 pCi/g 13981163 0.00196 pCi/g E‐13207 0.00783 pCi/g 14234356 ‐0.00722 pCi/g 15756328 0.00173 pCi/g 10098972 0.04 pCi/g 14133767 0.251 pCi/g 14274829 1.16 pCi/g 15594544 0.0376 pCi/g 14269637 0.863 pCi/g 7440291‐R 1.2 pCi/g 15065108 1.4 pCi/g 14913509 0.371 pCi/g 14333450 0.595 pCi/g 10028178 ‐0.382 pCi/g E‐13230 0.624 pCi/g E‐16045 0.0564 pCi/g 7440611‐R 0.613 pCi/g 10098916 0.04 pCi/g 14952400 ‐0.0848 pCi/g 14331830 1.11 pCi/g 14596102 0.00175 pCi/g 7440359 0.00703 pCi/g 14913496 0.844 pCi/g 14733030 0.864 pCi/g 14762755 ‐0.225 pCi/g 14336664 10.6 pCi/g 15757876/13981152 0.00175 pCi/g 10198400 0.00822 pCi/g 13967709 0.00511 pCi/g 10045973 0.0446 pCi/g 14683239 ‐0.0261 pCi/g 15585101 0.0155 pCi/g 14391163 0.0511 pCi/g 13967652 ‐0.00367 pCi/g 15046841 ‐0.00634 pCi/g 13966002 20.1 pCi/g 13966320 0.000346 pCi/g 14681631 0.00236 pCi/g E‐16032 ‐1.33 pCi/g E‐16033 0.0653 pCi/g 15700364 0.00858 pCi/g 13968597 0.0264 pCi/g 14331852 ‐0.336 pCi/g 15092941 1.33 pCi/g Page 2 of 3 Result  in SL  Units 0.666 1.01 1.02 0.37 ‐6.11 ‐0.752 0.62 0.0252 0.518 0.0292 0.0388 1.07 0.0135 ‐0.00232 0.808 0.862 ‐0.288 32.3 0.00582 ‐0.00177 ‐0.00148 0.0373 ‐0.00953 ‐0.0277 0.089 ‐0.013 0.0198 19.6 ‐0.0031 0.00435 ‐0.288 ‐0.354 ‐0.00514 0.037 0.0319 1.21 0.956 0.145 0.00196 0.00783 ‐0.00722 0.00173 0.04 0.251 1.16 0.0376 0.863 1.2 1.4 0.371 0.595 ‐0.382 0.624 0.0564 0.613 0.04 ‐0.0848 1.11 0.00175 0.00703 0.844 0.864 ‐0.225 10.6 0.00175 0.00822 0.00511 0.0446 ‐0.0261 0.0155 0.0511 ‐0.00367 ‐0.00634 20.1 0.000346 0.00236 ‐1.33 0.0653 0.00858 0.0264 ‐0.336 1.33 SL Detected Units pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g Y Y Y Y N N Y Y Y N N Y Y N Y Y N N N N N Y N N Y N N Y N N N N N N N Y Y N N Y N N N N Y Y Y Y Y Y N N Y Y Y N N Y Y Y Y Y N N N N N Y N N Y N N Y N N N N N N N Y Project  Qual  Validation Note Code U U U U U U U U U U U U J U U UJ U UJ U U U U U U U U U U U U U U U U U U U U U J U U UJ U UJ U U U U Boeing Soil Char Level  (pCi/g) 3.46 3.07 280 23100 ‐‐ 4.892 3.86 0.192 1.52 ‐‐ 2.5 679 1.8 ‐‐ 2800 7950 ‐‐ ‐‐ 0.331 0.0389 0.163 0.157 0.0406 0.0479 3.63 ‐‐ 1.134 26 0.0902 0.016 ‐‐ ‐‐ ‐‐ 626 0.562 3550 44800 ‐‐ 2.95 2.58 0.472 ‐‐ 0.24 ‐‐ 23.4 ‐‐ 3.46 3.07 280 23100 ‐‐ 4.892 3.86 0.192 1.52 ‐‐ 2.5 679 1.8 ‐‐ 2800 7950 ‐‐ ‐‐ 0.331 0.0389 0.163 0.157 0.0406 0.0479 3.63 ‐‐ 1.134 26 0.0902 0.016 ‐‐ ‐‐ ‐‐ 626 0.562 3550 Exceeds Boeing Soil Char Level No No No No No SL No No No No No SL No No No No SL No No No SL No SL No No No No No No No No SL No No No No No SL No SL No SL No No No No No SL No No No No SL No No SL No No SL No No No No No SL No No No No No SL No No No No SL No No No SL No SL No No No No No No No No SL No No No No No SL No SL No SL No No No Ratio Boeing Soil Char Level 1.92E‐01 3.29E‐01 3.64E‐03 1.60E‐05 No SL ‐1.54E‐01 1.61E‐01 1.31E‐01 3.41E‐01 No SL 1.55E‐02 1.58E‐03 7.50E‐03 No SL 2.89E‐04 1.08E‐04 No SL No SL 1.76E‐02 ‐4.55E‐02 ‐9.08E‐03 2.38E‐01 ‐2.35E‐01 ‐5.78E‐01 2.45E‐02 No SL 1.75E‐02 7.54E‐01 ‐3.44E‐02 2.72E‐01 No SL No SL No SL 5.91E‐05 5.68E‐02 3.41E‐04 2.13E‐05 No SL 6.64E‐04 3.03E‐03 ‐1.53E‐02 No SL 1.67E‐01 No SL 4.96E‐02 No SL 2.49E‐01 3.91E‐01 5.00E‐03 1.61E‐05 No SL ‐7.81E‐02 1.62E‐01 2.94E‐01 4.03E‐01 No SL ‐3.39E‐02 1.63E‐03 9.72E‐04 No SL 3.01E‐04 1.09E‐04 No SL No SL 5.29E‐03 2.11E‐01 3.13E‐02 2.84E‐01 ‐6.43E‐01 3.24E‐01 1.41E‐02 No SL ‐5.59E‐03 7.73E‐01 3.84E‐03 1.48E‐01 No SL No SL No SL 4.22E‐05 ‐5.98E‐01 3.75E‐04 SCL Basis EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG Background EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG Background EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG +D EPA Residential PRG EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background Background EPA Residential PRG EPA Residential PRG EPA Residential PRG Background EPA Residential PRG SCL Units +/‐ Error +/‐ Error  Units pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g 0.0623 0.0756 0.121 0.0173 4.29 1.54 0.0578 0.0156 0.0517 0.0493 0.0494 0.0416 0.0058 0.00519 0.0593 0.0304 0.197 32.9 0.00643 0.0044 0.00464 0.00774 0.0127 0.0267 0.0246 0.00654 0.0401 0.847 0.0053 0.00385 0.6 0.222 0.00981 0.0332 0.215 0.0558 0.0325 1.82 0.00438 0.00554 0.0116 0.00424 0.0896 0.402 0.0826 0.0221 0.0688 0.081 0.14 0.0182 3.82 1.61 0.0656 0.0226 0.0622 0.0896 0.054 0.0458 0.00302 0.00524 0.0751 0.0314 0.2 35.6 0.00392 0.00494 0.00477 0.00631 0.0143 0.0298 0.0197 0.00711 0.0422 0.869 0.00577 0.00404 0.68 0.264 0.0105 0.0349 0.232 0.0658 MDC 0.0515 0.0407 0.27 0.0135 12.5 5.64 0.0741 0.0376 0.0557 0.177 0.171 0.083 0.00524 0.0215 0.107 0.0267 0.677 114 0.0209 0.0147 0.0133 0.0155 0.041 0.0886 0.0586 0.0218 0.144 0.105 0.0175 0.0136 2.06 0.752 0.0321 0.115 0.712 0.0288 0.029 6.21 0.0144 0.0144 0.0387 0.0148 0.314 1.35 0.0779 0.0645 0.0395 0.0496 0.259 0.0155 11.4 5.81 0.109 0.0434 0.0848 0.314 0.18 0.0875 0.00473 0.00635 0.121 0.0311 0.682 121 0.0129 0.0176 0.0145 0.0157 0.0428 0.087 0.0654 0.024 0.161 0.11 0.0198 0.0139 2.2 0.878 0.0347 0.119 0.74 0.0309 Samples  Samples  MDC  Best  included in  included in  Units Pick? ERA HHRA pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Soil-RAD APPENDIX A2 Sample Locations and Analytical Data for EEL RFI Site ‐ Soil‐RAD RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California RFI Site EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL EEL Cluster EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 EEL CC 1 Object  Type Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Soil Boring Object Name A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 A3_SED_DG‐14 SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C SL‐143‐SA5C Sample Name (unique  Parent  Sample  ID or unique  Sample  ID designation) Name SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 10244 Sample Type Collection Date Matrix  Type Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample Primary Sample 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/5/11 14:55 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 10/20/10 14:00 Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Sample Top  Depth (feet bgs) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sample  Bottom  Depth (feet bgs) 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 Remediation  Status In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place In Place Result Type Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Primary Result Analytical Class Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Analysis  Method Analyte CAS Number Result  Value Result  Value  Units Result  in SL  Units SL Detected Units Lead‐214 Promethium‐147 Plutonium‐238 Plutonium‐239/240 Antimony‐125 Antimony‐126 Strontium‐90 Technetium‐99 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Thallium‐208 Thulium‐171 Tritium Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 Actinium‐228 Actinium‐227 Americium‐241 Barium‐137m Bismuth‐212 Bismuth‐214 Cadmium‐113m Curium‐243/244 Curium‐245/246 Curium‐247/248 Cobalt‐60 Cesium‐134 Cesium‐137 Europium‐152 Europium‐154 Europium‐155 Holmium‐166m Potassium‐40 Sodium‐22 Niobium‐94 Neptunium‐236 Neptunium‐239 Protactinium‐231 Lead‐212 Lead‐214 Plutonium‐236 Plutonium‐238 Plutonium‐239/240 Plutonium‐244 Radon‐220 Radon‐222 Antimony‐125 Antimony‐126 Strontium‐90 Tellurium‐125m Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Thallium‐208 Thulium‐171 Uranium‐233/234 Uranium‐235/236 Uranium‐238 15067284 14380757 13981163 E‐13207 14234356 15756328 10098972 14133767 14274829 15594544 14269637 7440291‐R 15065108 14913509 14333450 10028178 E‐13230 E‐16045 7440611‐R 10098916 14331830 14952400 14596102 378253408 14913496 14733030 14336664 15757876/13981152 15621768/15757901 15758324/15758335 10198400 13967709 10045973 14683239 15585101 14391163 13967652 13966002 13966320 14681631 15700364 13968597 14331852 15092941 15067284 15411924 13981163 E‐13207 14119347 22481487 20076011 14234356 15756328 10098972 14390739m 14274829 15594544 14269637 7440291‐R 15065108 14913509 14333450 E‐13230 E‐16045 7440611‐R 1.06 0.506 ‐0.00204 0.00409 0.025 0.00272 0.275 0.201 1.25 0.0454 0.798 1.1 1.52 0.391 0.225 2.32 0.68 0.0472 0.795 0.275 1.32 0.072 0 0.0267 1.1 0.99 9 0.00091 0 0 0.0064 0.0093 0.0283 ‐0.0034 0.013 0.08 0.0067 18.8 ‐0.0049 0.0049 ‐0.00004 ‐0.027 0.11 1.64 1.01 ‐0.0011 0.0011 0.00054 0.0022 1.37 1 0.119 ‐0.0043 0.001 0.0276 1.25 0.0039 0.958 1.23 1.76 0.545 0.1 0.852 0.0508 0.837 pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g 1.06 0.506 ‐0.00204 0.00409 0.025 0.00272 0.275 0.201 1.25 0.0454 0.798 1.1 1.52 0.391 0.225 2.32 0.68 0.0472 0.795 0.275 1.32 0.072 0 0.0267 1.1 0.99 9 0.00091 0 0 0.0064 0.0093 0.0283 ‐0.0034 0.013 0.08 0.0067 18.8 ‐0.0049 0.0049 ‐0.00004 ‐0.027 0.11 1.64 1.01 ‐0.0011 0.0011 0.00054 0.0022 1.37 1 0.119 ‐0.0043 0.001 0.0276 1.25 0.0039 0.958 1.23 1.76 0.545 0.1 0.852 0.0508 0.837 pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g Only chemicals identified as COPCs/ROPCs in Tables E1‐1 and E1‐2 were included in HHRA risk calculations. Only chemicals identified as CPECs/RPECs in Tables E2‐2 and E2‐17 were included in ERA risk calculations. Page 3 of 3 Y N N Y Y N Y N Y Y Y Y Y Y N N Y Y Y Y Y N N Y Y Y N N N N N N Y N N Y N Y N N N N N Y Y N N N Y Y Y Y N N Y Y N Y Y Y Y N Y Y Y Project  Qual  Validation Note Code U U J U U U U U U U U UJ UJ U U U U J U U U U U U U U U J U U J UJ U Boeing Exceeds Ratio Soil Char Boeing Boeing SCL Basis Level Soil Char Soil Char  (pCi/g) Level Level 44800 No 2.37E‐05 EPA Residential PRG ‐‐ No SL No SL 2.95 No ‐6.92E‐04 EPA Residential PRG 2.58 No 1.59E‐03 EPA Residential PRG 0.472 No 5.30E‐02 EPA Residential PRG ‐‐ No SL No SL 0.24 Yes 1.15E+00 EPA Residential PRG +D ‐‐ No SL No SL 23.4 No 5.34E‐02 EPA Residential PRG ‐‐ No SL No SL 3.46 No 2.31E‐01 EPA Residential PRG 3.07 No 3.58E‐01 EPA Residential PRG 280 No 5.43E‐03 EPA Residential PRG +D 23100 No 1.69E‐05 EPA Residential PRG ‐‐ No SL No SL 4.892 No 4.74E‐01 Background 3.86 No 1.76E‐01 EPA Residential PRG 0.192 No 2.46E‐01 EPA Residential PRG 1.52 No 5.23E‐01 Background ‐‐ No SL No SL 679 No 1.94E‐03 EPA Residential PRG 2.5 No 2.88E‐02 EPA Residential PRG 1.8 No 0.00E+00 EPA Residential PRG ‐‐ No SL No SL 2800 No 3.93E‐04 EPA Residential PRG +D 7950 No 1.25E‐04 EPA Residential PRG ‐‐ No SL No SL 0.331 No 2.75E‐03 EPA Residential PRG 0.391 No 0.00E+00 EPA Residential PRG ‐‐ No SL No SL 0.0389 No 1.65E‐01 EPA Residential PRG 0.163 No 5.71E‐02 EPA Residential PRG 0.157 No 1.80E‐01 Background 0.0406 No ‐8.37E‐02 EPA Residential PRG 0.0479 No 2.71E‐01 EPA Residential PRG 3.63 No 2.20E‐02 EPA Residential PRG ‐‐ No SL No SL 26 No 7.23E‐01 Background 0.0902 No ‐5.43E‐02 EPA Residential PRG 0.016 No 3.06E‐01 EPA Residential PRG ‐‐ No SL No SL 626 No ‐4.31E‐05 EPA Residential PRG 0.562 No 1.96E‐01 Background 3550 No 4.62E‐04 EPA Residential PRG 44800 No 2.25E‐05 EPA Residential PRG ‐‐ No SL No SL 2.95 No 3.73E‐04 EPA Residential PRG 2.58 No 2.09E‐04 EPA Residential PRG ‐‐ No SL No SL 786000000 No 1.74E‐09 EPA Residential PRG ‐‐ No SL No SL 0.472 No 2.52E‐01 EPA Residential PRG ‐‐ No SL No SL 0.24 No 4.17E‐03 EPA Residential PRG +D ‐‐ No SL No SL 23.4 No 5.34E‐02 EPA Residential PRG ‐‐ No SL No SL 3.46 No 2.77E‐01 EPA Residential PRG 3.07 No 4.01E‐01 EPA Residential PRG 280 No 6.29E‐03 EPA Residential PRG +D 23100 No 2.36E‐05 EPA Residential PRG ‐‐ No SL No SL 3.86 No 2.21E‐01 EPA Residential PRG 0.192 No 2.65E‐01 EPA Residential PRG 1.52 No 5.51E‐01 Background SCL Units +/‐ Error +/‐ Error  Units pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g 0.0372 1.97 0.00354 0.00409 0.0125 0.00458 0.0786 0.325 0.0894 0.0196 0.07 0.0796 0.162 0.0186 4.63 1.74 0.0606 0.0218 0.0637 0.0786 0.027 0.046 0.002 0.0066 0.081 0.02 13 0.00091 0.00095 0.0012 0.005 0.003 0.007 0.0041 0.031 0.016 0.0052 0.21 0.0063 0.0045 0.009 0.028 0.098 0.016 0.016 0.0016 0.0011 0.00054 0.0011 0.08 0.026 0.009 0.0052 0.016 0.0022 0.031 0.0057 0.027 0.031 0.075 0.014 2.1 0.027 0.0073 0.027 MDC 0.0323 6.71 0.0151 0.00554 0.0425 0.0158 0.227 1.09 0.0968 0.0417 0.0742 0.0415 0.28 0.0157 13.9 5.82 0.0729 0.0545 0.053 0.227 0.09 0.15 0.0087 0.014 0.15 0.029 42 0.0025 0.0023 0.0061 0.016 0.058 0.015 0.037 0.1 0.039 0.026 0.18 0.021 0.015 0.03 0.092 0.61 0.026 0.027 0.0071 0.004 0.0015 0.0015 0.03 0.027 0.043 0.017 0.054 0.01 0.016 0.021 0.006 0.006 0.17 0.021 6.9 0.008 0.0029 0.006 Samples  Samples  MDC  Best  included in  included in  Units Pick? ERA HHRA pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Y Appendix B Air Dispersion Modeling and Sampling Summary No Boeing sources were identified as requiring air dispersion modeling at the EEL RFI site, so Appendix B is  not provided in this report.   Appendix C Potential Transport of Contaminants in the Vadose Zone to Groundwater for EEL RFI Site Draft APPENDIX C: POTENTIAL TRANSPORT OF CONTAMINANTS IN VADOSE ZONE TO GROUNDWATER ENVIRONMENTAL EFFECTS LABORATORY RFI SITE SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA Prepared For: THE BOEING COMPANY Prepared By: MWH 2121 N. California Blvd., Suite 600 Walnut Creek, CA 94596 June 10, 2015 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 EXECUTIVE SUMMARY This Appendix C: Potential Transport of Contaminants in Vadose Zone to Groundwater for the Environmental Effects Laboratory (EEL) Resource Conservation and Recovery Act (RCRA) Facility Investigation (RFI) Site located within Subarea 5/9 South at Santa Susana Field Laboratory (SSFL) in Ventura County, California, was completed in accordance with the Comprehensive Data Quality Objectives (DQOs) developed for SSFL (DQO Report, CH2M HILL, 2013) to support completion of Boeing’s RFI and subsequent transition to the corrective measures study (CMS). The objective of this report is to document methodologies used in performing the transport of contaminants from the vadose zone to groundwater evaluation for the EEL RFI Site and provide detailed results of the evaluation. The evaluation was performed to identify chemicals in the vadose zone requiring further evaluation in the CMS for the protection of groundwater for site-related chemicals that have either impacted groundwater or been identified as a potential threat to groundwater in the future. The vadose zone to groundwater evaluation involved a comprehensive review of vadose zone and groundwater data, and vadose zone to groundwater transport modeling at the EEL RFI Site for one Chemical Use Area (CUA) Cluster (CC): EEL CC 1. The evaluation summary and recommendations are presented below and in the Vadose Zone to Groundwater Evaluation Executive Summary table (Table CES-1). Chemical Use Area Cluster Total Number of Chemicals Evaluated in the Vadose Zone Total Number of Chemicals Recommended for No Further Action (NFA) 209 Chemicals Recommended for CMS in the Vadose Zone for Protection of Groundwater • trichloroethene (TCE) • perchlorate • 2,4-dichlorophenoxybutyric acid (DB) • methylchlorophenoxypropionic acid (MCPA) • beta-benzene hexachlorocyclohexane (BHC) • heptachlor • heptachlor epoxide • nitrate-NO3 Note: Separate gasoline range organics (GRO), kerosene range organics (KRO), diesel range organics (DRO), and oil range organics ranges (ORO) hydrocarbon ranges are counted together as one, respectively for each fuel type. EEL CC 1 217 ES-1 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 TABLE OF CONTENTS Section Page EXECUTIVE SUMMARY..................................................................................................... ES-1 C.1 INTRODUCTION ................................................................................................................ C-1 C.2 VADOSE ZONE TO GROUNDWATER EVALUATION METHODOLOGY .............................. C-2 C.2.1 Vadose Zone Data Evaluation Methodology ............................................................................... C-2 C.2.2 Groundwater Data Evaluation Methodology ............................................................................... C-2 C.2.3 Transport Modeling Evaluation Methodology ............................................................................. C-4 C.2.3.1 Transport from the Vadose Zone to Groundwater ............................................................... C-5 C.2.3.2 Protection of Groundwater ................................................................................................... C-5 C.2.4 Approach for Identifying CMS Areas.......................................................................................... C-6 C.3 FIELD WORK ................................................................................................................... C-7 C.4 VADOSE ZONE TO GROUNDWATER EVALUATION RESULTS .......................................... C-8 C.4.1 Vadose Zone Data Evaluation Results ......................................................................................... C-8 C.4.2 Groundwater Data Evaluation Results ......................................................................................... C-9 C.4.3 Transport Modeling Evaluation Results .................................................................................... C-10 C.4.3.1 Transport from the Vadose Zone to Groundwater ............................................................. C-11 C.4.3.2 Protection of Groundwater ................................................................................................. C-11 C.5 RECOMMENDATIONS ..................................................................................................... C-12 REFERENCES ........................................................................................................................ C-15 i Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 LIST OF FIGURES Figure C-1 Figure C-2 Figure C-3 Figure C-4 Figure C-5 Vadose Zone to Groundwater Evaluation Methodology Vadose Zone CMS Recommendations for Protection of Groundwater Methodology Particle Tracks for Evaluating Groundwater Flow, EEL RFI Site Vertical Profile of the Vadose Zone, EEL RFI Site SESOIL Thickness Contour and Groundwater Recharge Maps, EEL RFI Site LIST OF TABLES Table C-ES-1 Table C-1 Table C-2 Table C-3 Vadose Zone to Groundwater Evaluation Executive Summary Vadose Zone and Groundwater Data Evaluation Summary Vadose Zone to Groundwater Transport Modeling Results Summary Protection of Groundwater Transport Modeling Results Summary LIST OF ATTACHMENTS Attachment C-1 Attachment C-2 Attachment C-3 Attachment C-4 Attachment C-5 Attachment C-6 Estimate of Transport Distances based on Darcy Flux SESOIL Transport Modeling Inputs and Assumptions Monitoring Well RS-37 Boring Log, Well Construction Diagram, and Well Development Log Summary of Radiological Data at the EEL RFI Site Additional Data Assessment, EEL RFI Site SESOIL Transport Modeling Output Report, EEL RFI Site ii Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site LIST OF ABBREVIATIONS AND ACRONYMS BHC benzene hexachlorocyclohexane BTVs background threshold values bgs below ground surface CC chemical use area cluster CMS corrective measures study CUA chemical use area DOE Department of Energy DTSC Department of Toxic Substances Control DB dichlorophenoxybutyric acid DNAPL dense non-aqueous phase liquid DQOs data quality objectives DRO diesel range organics EMLC estimated maximum leachate concentration EEL Environmental Effects Laboratory GCVs groundwater comparison values GRO gasoline range organics HVZC highest vadose zone concentration KRO kerosene range organics LCV leachate comparison value MCPA methylchlorophenoxypropionic acid m/s meters per second NFA no further action NDMA n-nitrosodimethylamine ORO oil range organics PAHs polycyclic aromatic hydrocarbons PCBs polychlorinated biphenyl RCRA Resource Conservation and Recovery Act RFI RCRA facility investigation SESOIL seasonal soil compartment model iii DRAFT June 2015 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site SSFL Santa Susana Field Laboratory SVOCs semi-volatile organic compounds TCE trichloroethene VOCs volatile organic compounds iv DRAFT June 2015 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site C.1 DRAFT June 2015 Introduction This Appendix C: Potential Transport of Contaminants in Vadose Zone to Groundwater for the Environmental Effects Laboratory (EEL) Resource Conservation and Recovery Act (RCRA) Facility Investigation (RFI) Site located within Subarea 5/9 South at Santa Susana Field Laboratory (SSFL) in Ventura County, California, was completed in accordance with the Comprehensive Data Quality Objectives (DQOs) developed for SSFL (DQO Report, CH2M HILL, 2013) to support completion of Boeing’s RFI and subsequent transition to the corrective measures study (CMS). The objective of this report is to document methodologies used in performing the transport of contaminants from the vadose zone to groundwater evaluation for the EEL RFI Site and provide detailed results of the evaluation. The evaluation was performed to identify chemicals in the vadose zone requiring further evaluation in the CMS for the protection of groundwater for site-related chemicals that have either impacted groundwater or been identified as a potential threat to groundwater in the future. This report is organized as follows: • Section C-1 Introduction – presents the report objective and organization • Section C.2 Vadose Zone to Groundwater Evaluation Methodology – provides a summary of the methods used for the evaluation; • Section C.3 Field Work – provides a summary of field work performed to fill data gaps identified as part of this evaluation; • Section C.4 Vadose Zone to Groundwater Evaluation Results – presents the results of the evaluation; and • Section C.5 Recommendations – presents CMS recommendations based on the evaluation performed. The vadose zone to groundwater evaluation involved a comprehensive review of vadose zone and groundwater data, and vadose zone to groundwater transport modeling at the EEL RFI Site for one Chemical Use Area (CUA) Cluster (CC): EEL CC 1. C-1 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site C.2 DRAFT June 2015 Vadose Zone to Groundwater Evaluation Methodology This section presents detailed methods used to identify site-related chemicals that have either impacted groundwater or been identified as a potential threat to groundwater in the future. The methodologies used are summarized in flow charts provided as Figure C-1 and Figure C-2. C.2.1 Vadose Zone Data Evaluation Methodology Available soil matrix and soil vapor vadose zone data were evaluated for the EEL RFI Site. These data were first screened against either Background Threshold Values (BTVs) or Groundwater Comparison Values (GCVs) as presented in Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (MWH, 2013; Appendix D of the DQO Report [CH2M HILL, 2013]) with applicable updates to regulatory screening levels if the updated levels are lower than those presented in that report. Additional screening levels were developed and documented in the Final Development of Risk Based Screening Levels for Additional Groundwater Constituents and Screening Level Clarifications (MWH, 2014b) and Draft Development of Risk Based Screening Levels for Additional Groundwater Constituents Detected at the Santa Susana Field Laboratory (MWH, 2014d). Consistent with the DQO framework and the Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (MWH, 2013), BTVs were used for screening of vadose zone data, if available, and GCVs were used if BTVs were not available. The findings from this evaluation are documented as follows: 1. Chemicals with Exceedances in the Vadose Zone – Chemicals that exceeded their respective BTVs or GCVs in the vadose zone samples are documented in Table C-1 under the vadose zone data evaluation section and carried forward to the groundwater data evaluation. 2. Chemicals with No Exceedances in the Vadose Zone – Chemicals that were either not detected or detected at or below their respective BTVs or GCVs in vadose zone samples are documented in Table C-ES-1 and recommended for no further action (NFA). C.2.2 Groundwater Data Evaluation Methodology Chemicals that exceeded their BTVs or GCVs in vadose zone samples were further evaluated to determine their presence in groundwater. Recent groundwater data (defined as data collected from 2010 to 2014) for these chemicals in samples collected from monitoring wells located within approximately C-2 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 300 feet of the CC boundary and interpreted to intercept flow from the CC were screened against their respective GCVs. Wells were selected by using the three-dimensional groundwater flow model developed for SSFL as presented in the 2009 Draft Site-Wide Groundwater Remedial Investigation Report (MWH, 2009). Flow paths as represented by particle tracking methods were used to help evaluate groundwater flow directions at the EEL RFI Site. The flow model was used to create forward and backward particle tracks (i.e., flow paths). The forward particle tracks depict how groundwater moves from source areas through the flow field. CC-specific forward particle tracks were developed for this evaluation to evaluate flow paths from the CC at EEL. The backward particle tracks depict how groundwater moves through the flow field from a location (e.g., well) to its area of capture. Forward and backward particle tracking for both non-pumping and pumping conditions were reviewed, where the pumping condition represents a period of groundwater extraction at SSFL between 1995 and 1998. The forward particle tracking generated by the flow model represent groundwater flow paths to depths of either 10 or 200 meters below the water table. Particle releases at the water table to depths of 10 meters (33 feet) below the water table are used to represent chemicals released as solutes. Particle releases to depths of 200 meters (656 feet) below the water table are used to represent the transport of potential releases of dense non-aqueous phase solvents (DNAPL) such as trichloroethene (TCE). The 0to 10-meter flow paths are used to help interpret flow directions if there were no known DNAPL releases at a CC. The 0- to 200-meter flow paths are used if there was a known historical DNAPL release at a CC. The 0- to 10-meter particle tracks were used for EEL CC 1 because there is no indication in historical records or apparent in the characterization data that indicates DNAPL releases within the CC. The backward particle tracks illustrate the entire flow path and direction from the recharge area to the well location at depth locations across the open or screened interval of the well. The particle tracks were generated to a flowpath length of 1,000 meters as site data and contaminant transport simulations show this to be a reasonable upper bound estimate of plume extent. To estimate the extent of chemical transport from likely or confirmed sources at an RFI Site, the length of forward particles paths (i.e., paths starting at sources and advancing through the flow field) were truncated based on the mean Darcy flux under both pumping and non-pumping conditions. The Darcy flux along the particle paths generated for an RFI Site is equal to the total particle track length divided by the time it takes to flow along the flowpath based on a porosity of 1. The average of the computed Darcy flux values for particle paths under non-pumping and pumping conditions for EEL was 4.63x10-10 meters per second C-3 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site (m/s) and 4.28x10-10 m/s, respectively. DRAFT June 2015 Results from contaminant transport simulations for three RFI sites at SSFL [as presented in the Draft Site-Wide Groundwater Remedial Investigation Report (MWH, 2009)] were used to create a plot of transport distance versus mean Darcy flux. A plot for the nonpumping and pumping conditions is provided in Attachment C-1. The mean Darcy flux for each RFI Site was then plotted and the estimated transport distance was taken from where the point intersects the horizontal axis. Forward particle paths for EEL were truncated to 135 and 130 meters for the nonpumping and pumping conditions, respectively, as shown in Figure C-3. These estimated transport distances represent an upper bound estimate of the extent of contaminant distribution to site characterization levels at a time 50 years after a release. Wells interpreted to intercept groundwater flow from EEL were identified based on review of these truncated particle tracks. Chemicals with exceedances in the vadose zone were screened against GCVs for recent groundwater data (from 2010 to 2014) from well locations interpreted to monitor the EEL CC (intercept flow paths from the CC) and contain groundwater representative of the EEL CC (not interpreted to be primarily impacted by an adjacent RFI site or CC). Figure C-3 provides a depiction of the EEL CC, vadose zone sample locations, well locations, and flow model forward and backward particle tracks. The findings from this evaluation are documented as follows: 1. Chemicals with Exceedances in the Vadose Zone but not in Groundwater – Chemicals detected at concentrations that exceeded their respective BTVs or GCVs in vadose zone samples but were not detected or detected at or below their respective GCVs in groundwater samples are documented in Table C-1 under the groundwater data evaluation section and further evaluated in the transport modeling evaluation for transport from the vadose zone to groundwater. 2. Chemicals with Exceedances in both the Vadose Zone and Groundwater – Chemicals detected at concentrations that exceeded their respective BTVs or GCVs in the vadose zone samples and also exceeded their respective GCVs in groundwater samples are documented in Table C-1 under the groundwater data evaluation section and are further evaluated in the transport modeling evaluation for protection of groundwater. C.2.3 Transport Modeling Evaluation Methodology Transport modeling was performed using the Seasonal Soil compartment model (SESOIL) in accordance with the Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to C-4 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 Groundwater (MWH, 2013; Appendix D of the DQO Report [CH2M HILL, 2013]). SESOIL is a onedimensional vertical transport screening-level model for the vadose zone that is designed to simulate fate and transport of chemical compounds based on diffusion, adsorption, volatilization, biodegradation, cation exchange, and hydrolysis. A description of SESOIL transport modeling inputs and assumptions is provided in Attachment C-2. The vadose zone transport column for EEL CC 1 is presented in Figure C-4. The vadose zone transport column developed for each CC represents a compilation of many data points and reflects general conditions rather than a specific, unique location within the cluster. Soil thickness contours and groundwater recharge values for EEL CC 1 are presented in Figure C-5. C.2.3.1 Transport from the Vadose Zone to Groundwater For chemicals that exceeded their respective BTVs or GCVs in vadose zone samples but were not detected or detected at or below their respective GCVs in groundwater samples, an estimated maximum leachate concentration (EMLC) was calculated for each of these chemicals to determine whether chemicals would leach from the vadose zone to groundwater at concentrations above their GCVs. The findings from this evaluation are documented in Table C-2 as follows: 1. Chemicals with Predicted Leachate Exceedances – Chemicals with predicted EMLCs greater than their respective GCVs are predicted to reach groundwater at concentrations above their GCVs based on the transport modeling evaluation and are further evaluated for future protection of groundwater. 2. Chemicals with No Predicted Leachate Exceedances – Chemicals with predicted EMLCs less than or equal to their respective GCVs are not predicted to reach groundwater at concentrations above their GCVs based on the transport modeling evaluation and are recommended for NFA. C.2.3.2 Protection of Groundwater Chemicals that exceeded their respective screening levels in both the vadose zone and groundwater and chemicals with predicted EMLCs greater than their respective GCVs in the transport from vadose zone to groundwater evaluation were further evaluated for protection of groundwater. For each chemical, the highest vadose zone concentration (HVZC) that could remain without producing leachate at a C-5 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 concentration above its leachate comparison value (LCV) was calculated using SESOIL, and available vadose zone data were screened against the calculated HVZC. The LCV equals the GCV for chemicals with no Department of Toxic Substances Control (DTSC) established BTV and the higher value between GCV and modeled leachate concentration generated by loading the BTV throughout the vadose zone profile for chemicals where a Department of Toxic Substances Control (DTSC) established BTV is available. The approach for identifying chemicals requiring further evaluation for protection of groundwater (vadose zone CMS recommendations) is summarized in Figure C-2 and the findings from this evaluation are documented in Table C-3 as follows: 1. Chemicals with Exceedances of Vadose Zone Concentrations Protective of Groundwater – Chemicals with vadose zone concentrations exceeding their respective HVZCs are identified as requiring further evaluation for protection of groundwater and are recommended for CMS. 2. Chemicals with No Exceedances of Vadose Zone Concentrations Protective of Groundwater but with Exceedances in Groundwater – Chemicals with no vadose zone concentrations exceeding their respective HVZCs but present in groundwater at wells interpreted to monitor and contain groundwater representative of the CC at concentrations above their respective GCVs are identified as requiring no further evaluation for protection of groundwater and are recommended for NFA. These chemicals are evaluated for their presence in groundwater above GCVs in the Groundwater Source Zone and Plume Characterization (Appendix D of this report). 3. Chemicals with No Exceedances of Vadose Zone Concentrations Protective of Groundwater and No Exceedances in Groundwater – Chemicals with no vadose zone concentrations exceeding their respective HVZCs and not present in groundwater at wells interpreted to monitor and contain groundwater representative of the CC at concentrations above their respective GCVs are identified as requiring no further evaluation for protection of groundwater and are recommended for NFA. C.2.4 Vadose Zone CMS Area Methodology The vadose zone CMS areas and locations include soil, soil vapor, and rock pore water sample locations that are interpreted to pose a potential threat to groundwater based on the data evaluation and transport modeling results presented in Table C-3. The criteria used to determine CMS areas and locations include consideration of chemical concentrations relative to the vadose zone screening values and background ranges identified in the soil background study (URS, 2012), transport modeling results, spatial data C-6 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 distribution, site features such as drainages and faults, and historical activities. Using these criteria, CMS areas are drawn where data is sufficient to delineate a boundary around locations with exceedances of vadose zone concentrations that are protective of groundwater as determined by the modeling. For cases where there are isolated detections of chemicals in exceedance of vadose zone concentrations protective of groundwater and the data is not sufficient to delineate an area, the individual sample location is displayed as a CMS location. C.3 Field Work This section presents a summary of the field work performed in response to the data gaps that were identified during the vadose zone to groundwater evaluation. Field work for EEL included installation of one groundwater monitoring well and groundwater sampling. Samples could not be collected from a number of existing wells at EEL due to being dry or containing insufficient water. As a result, the well network in the vicinity of the site was evaluated to assess the need for installing a well of sufficient depth to allow for groundwater sample collection. The evaluation revealed that dry well RS-17 was positioned to intercept likely flow paths from CC-01 under the nonpumping condition but was dry or had insufficient water for sampling. A recommendation was made to install a new well of sufficient depth near well RS-17 so that groundwater samples could be collected at that location. A new well (RS-37) was installed in December 2013 to satisfy the non-pumping condition. Bottom depth of the screen is 43 feet below ground surface (bgs) and the initial depth to water after development was 18.42 feet bgs. The well was constructed with sufficient screen to allow for fluctuations in groundwater levels that are expected due to temporal recharge variability. The well was developed in accordance with Section 9 of Standard Operating Procedure 16A prior to sampling (Boeing, 2013). The location of RS-37 is shown on Figure C-3. The boring log, well construction diagram, and well development log for RS-37 are provided in Attachment C-3. The following sampling recommendations (location – analyses) were made based on the vadose zone to groundwater evaluation for EEL: • ES-29 – semi-volatile organic compounds (SVOCs), polycyclic aromatic hydrocarbons (PAHs), diesel range organics (DRO), oil range organics (ORO), polychlorinated biphenyls (PCBs), dioxins/furans, herbicides, pesticides, and metals C-7 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 • PZ-050 – SVOCs, PAHs, ORO, PCBs, dioxins/furans, herbicides, pesticides, and metals • RS-17 – SVOCs, DRO, metals • RS-37 – volatile organic compounds (VOCs), SVOCs, PAHs, DRO, ORO, PCBs, dioxins/furans, herbicides, pesticides, and metals Groundwater samples were collected at wells RS-37 and ES-29 during the first and third quarters of 2014 and analyzed for the requested analytes. Samples were collected at PZ-050 during the third quarter of 2014, but sampling procedures were modified since there was insufficient water to sample using low flow methods. A bailer was used to dewater the well and samples were collected by bailing water that recharged into the well. Groundwater level monitoring, sampling, and analysis were conducted in accordance with the Field Sampling Plan and Quality Assurance and Project Plan for groundwater (Appendices of the Regulated Unit and Site-Wide Program Water Quality Sampling and Analysis Plans (H&A, 2010a; 2010b)), with the exception of the modified sampling method at PZ-050. Results for these wells and piezometer are reported in the quarterly and/or annual groundwater monitoring and sampling reports (MWH 2014a, 2014c, 2014e 2015). C.4 Vadose Zone to Groundwater Evaluation Results This section presents a summary of results of the vadose zone data, groundwater data, and transport modeling evaluations. Recommendations based on the evaluation of results are provided at the end of this section. Radiological data collected at the EEL RFI Site were evaluated separately, as radionuclides are not a known source at the site. Evaluation of radiological data for the EEL RFI Site is presented in Attachment C-4. Additional vadose zone data collected by the United States Department of Energy (DOE) at the EEL RFI Site were provided to Boeing after preparation of the EEL RFI Site Data Summary and Findings Report had commenced, and were therefore evaluated separately in a qualitative nature only. An assessment of the additional data is presented in Attachment C-5. C.4.1 Vadose Zone Data Evaluation Results Two-hundred fourteen (214) chemicals were evaluated in the vadose zone data evaluation from soil matrix and soil vapor sample locations at the EEL RFI Site for one CC: EEL CC 1 according to C-8 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 methodology described in Section C.2.1. A summary of the vadose zone data evaluation results is presented below. Chemical Use Area Cluster Total Number of Chemicals with Exceedances in the Vadose Zone Chemicals with Exceedances in the Vadose Zone Total Number of Chemicals with No Exceedances in the Vadose Zone Recommended for NFA 148 carried forward to Groundwater Data Evaluation • 1 VOC • 1 SVOC • 17 PAHs • 1 energetic (perchlorate) • DRO • ORO • 3 herbicides • 10 pesticides • 2 PCBs • 17 dioxins and furans • 15 metals Note: Separate gasoline range organics (GRO), kerosene range organics (KRO), diesel range organics (DRO), and oil range organics ranges (ORO) hydrocarbon ranges are counted together as one, respectively for each fuel type. EEL CC 1 69 Benzo(ghi)perylene and calcium exceeded their BTVs but were not evaluated further because they do not have a GCV established. Benzo(ghi)perylene is a potential human health concern but no toxicity criterion is available for it. Calcium is not recognized as a human health concern. Chemicals with exceedances in the vadose zone are presented in Table C-1 under the vadose zone data evaluation section and are carried forward to the groundwater data evaluation. Chemicals that were either not detected or detected at or below their respective BTVs or GCVs in the vadose zone are listed in Table C-ES-1 and recommended for NFA. C.4.2 Groundwater Data Evaluation Results The groundwater data evaluation of available data from 2010 to 2014 (with preliminary first quarter 2015 data at select wells) was performed according to the methodology described in Section C.2.2. The following well locations interpreted to monitor the EEL CC (intercept flow paths from the CC) and contain groundwater representative of the EEL CC (not interpreted to be primarily impacted by an adjacent RFI site or CC) were selected for the evaluation: C-9 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site Chemical Use Area Cluster EEL CC 1 Wells Selected for Evaluation ES-28, ES-29, ES-30, PZ-038, PZ-050, RS-15, RS-17, RS-37 DRAFT June 2015 Wells with Available Groundwater Data from 2010 to 2014 (with preliminary first quarter data at select wells) for Chemicals with Exceedances in the Vadose Zone ES-29, ES-30, PZ-050, RS-15, RS-17, RS-37 Figure C-2 provides a depiction of the EEL CC, vadose zone sample locations, well locations, and flow model particle tracks. A summary of the groundwater data evaluation results is presented below. Chemical Use Area Cluster Total Number of Chemicals with Exceedances in the Vadose Zone but not in Groundwater carried forward to Transport Modeling for Transport from Vadose Zone to Groundwater 54 Total Number of Chemicals with Exceedances in both the Vadose Zone and in Groundwater Chemicals with Exceedances in both the Vadose Zone and in Groundwater - Well Location(s) carried forward to Transport Modeling for Protection of Groundwater • TCE – at wells ES-29, ES-30, and RS-15 • DRO – at wells PZ-050 and ES-30 • Cadmium – at well PZ-050 • Manganese – at wells PZ-050 Note: Separate GRO, KRO, DRO, and ORO hydrocarbon ranges are counted together as one, respectively for each fuel type. EEL CC 1 4 Chemicals with exceedances in the vadose zone but not in groundwater are further evaluated in the transport modeling evaluation for transport from the vadose zone to groundwater. Chemicals with exceedances in both the vadose zone and groundwater are further evaluated in the transport modeling evaluation for protection of groundwater. These results are listed in Table C-1 and Table C-ES-1 under the groundwater data evaluation sections. C.4.3 Transport Modeling Evaluation Results Chemicals exceeding their respective BTVs or GCVs in the vadose zone were considered as a potential threat to groundwater and are further evaluated by transport modeling according to the methodology described in Section C.2.3. C-10 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 C.4.3.1 Transport from the Vadose Zone to Groundwater Chemicals that exceeded their respective BTVs or GCVs in vadose zone samples but were not detected or detected at or below their respective GCVs in groundwater samples were further evaluated by transport modeling for transport from the vadose zone to groundwater according to methodology described in Section C.2.3.1. A summary of transport modeling results for transport from the vadose zone to groundwater is presented below. Total Number of Total Number of Chemicals with Chemicals with Chemicals with Predicted Leachate Exceedances Predicted Leachate No Predicted Leachate Exceedances Exceedances carried forward to Transport Modeling for Protection of Groundwater Recommended for NFA EEL CC 1 12 62 • One energetic (perchlorate) • Two herbicides (2,4- dichlorophenoxybutyric acid [DB], methylchlorophenoxypropionic acid MCPA) • Three pesticides (beta- benzene hexachlorocyclohexane [BHC], heptachlor, heptachlor epoxide) • Four metals (barium, mercury, silver, sodium) • Two inorganics (fluoride, nitrate-no3) Note: Separate GRO, KRO, DRO, and ORO hydrocarbon ranges are counted together as one, respectively for each fuel type. Chemical Use Area Cluster Chemicals with predicted EMLCs that exceeded their respective GCVs during the 100 year simulation are predicted to reach groundwater at concentrations above their GCVs based on the transport modeling evaluation and are further evaluated for future protection of groundwater. Chemicals with predicted EMCLs that did not exceed their applicable GCVs at any time during the 100 year simulation are not predicted to reach groundwater at concentrations above their GCVs based on the transport modeling evaluation and are recommended for NFA. The detailed evaluation for transport modeling for transport of chemicals from the vadose zone to groundwater is presented in Table C-2 and SESOIL modeling results are provided in Attachment C-6. C.4.3.2 Protection of Groundwater Chemicals that exceeded their respective screening values in both the vadose zone and groundwater and chemicals with predicted EMLCs greater than their respective GCVs in the transport from vadose zone to groundwater evaluation were evaluated to identify chemicals requiring further evaluation for protection of groundwater according to methodology described in Section C.2.3.2. Sixteen chemicals (four chemicals exceeding in both the vadose zone and groundwater and 12 chemicals with EMLC greater than GCVs) C-11 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 were subject to this evaluation for EEL CC 1. A summary of transport modeling results for protection of groundwater is presented below. Chemical Use Area Cluster Total Number of Chemicals with Exceedances of Vadose Zone Concentrations Protective of Groundwater Chemicals with Exceedances of Vadose Zone Concentrations Protective of Groundwater and Number and Type of Vadose Zone Samples Recommended for CMS for protection of groundwater Total Number of Chemicals with No Exceedances of Vadose Zone Concentrations Protective of Groundwater but with Exceedances in Groundwater Recommended for NFA 3 Total Number of Chemicals with No Exceedances of Vadose Zone Concentrations Protective of Groundwater and No Exceedances in Groundwater Recommended for NFA 3 • TCE – at 3 soil vapor sample locations • Perchlorate – at 1 soil sample location • 2,4-DB – at 1 soil sample location • MCPA- at 1 soil sample location • Beta-BHC – at 1 soil sample location • Heptachlor • Heptachlor epoxide • Nitrate-NO3 Note: Separate GRO, KRO, DRO, and ORO hydrocarbon ranges are counted together as one, respectively for each fuel type. EEL CC 1 8 Chemicals with vadose zone concentrations exceeding their respective HVZCs are identified as requiring further evaluation for protection of groundwater and are recommended for CMS. Chemicals with no vadose zone concentrations exceeding their respective HVZCs but present in groundwater at concentrations above their respective GCVs are identified as requiring no further evaluation for protection of groundwater and are recommended for NFA. These chemicals are evaluated for their presence in groundwater above GCVs in the Groundwater Source Zone and Plume Characterization (Appendix D of this report). Chemicals with no vadose zone concentrations exceeding their respective HVZCs and not present in groundwater at concentrations above their respective GCVs are identified as requiring no further evaluation for protection of groundwater and are recommended for NFA. Sample identifications, EMLCs based on the maximum vadose zone concentrations, and the chemicals’ calculated HVZCs are presented in Table C-3 and SESOIL modeling results are provided in Attachment C-6. C.5 Recommendations Chemicals with vadose zone concentrations exceeding their respective HVZCs are identified as requiring further evaluation for protection of groundwater and are recommended for CMS. Two vadose zone CMS areas and two CMS locations were identified for the EEL RFI Site and are listed below. C-12 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 Vadose Zone CMS Areas: • EEL-CMS-VZ1 (TCE, perchlorate) • EEL-CMS-VZ2 (TCE, 2,4-DB, and heptachlor epoxide) The following were identified as vadose zone CMS locations due to their isolation from other exceedances and lack of sufficient data to delineate an area. Vadose Zone CMS Locations: • beta-BHC (ELBS2000) • heptachlor (ELBS2000) • perchlorate (SL-143-SA5C) • MCPA (ELBS2000, SL-143-SA5C) • nitrate-NO3 (ELBS2035) The vadose zone CMS location SL-143-SA5C was included based on a qualitative analysis performed on additional data collected at the site for the DOE. The qualitative analysis is presented in Attachment C-6. The transport modeling conducted for the vadose zone to groundwater evaluation produced highly conservative results for chemicals that readily degrade because the transport model does not account for biodegradation. Thus, it is recommended that the vadose zone CMS areas and locations presented above be revisited during the CMS to consider natural attenuation processes. The following chemicals are recommended for groundwater monitoring at the EEL RFI Site every five years for arrival in groundwater based on model predictions. Chemical Use Area Cluster EEL CC 1 Chemical • • • • • • • • • • • • perchlorate 2,4-DB MCPA beta-BHC heptachlor heptachlor epoxide barium mercury silver sodium fluoride nitrate-no3 Well Locations ES-28, ES-29, ES-30, PZ-038, PZ-050, RS-15, RS-17, and RS-37 C-13 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 Results and recommendations for each chemical evaluated are provided in the Vadose Zone to Groundwater Evaluation Executive Summary (Table C-ES-1) and vadose zone CMS areas and locations are depicted in Figure 6-1 of the main body of this report. C-14 Appendix C: Potential Transport of Contaminants in Vadose Zone To Groundwater Environmental Effects Laboratory RFI Site DRAFT June 2015 REFERENCES Boeing, 2013. Standard Operating Procedures for Areas I and III of the Santa Susana Field Laboratory, Ventura County, CA. March. CH2M HILL, 2013. Comprehensive Data Quality Objectives, RCRA Field Investigation Santa Susana Field Laboratory, Ventura County, CA. March. Haley & Aldrich, Inc. (H&A), 2010a. Regulated Unit Water Quality Sampling and Analysis Plan, Areas I and III, Post-Closure Permit PC-94/95-3-02, Santa Susana Field Laboratory, Ventura County, California. April. H&A, 2010b. Site-Wide Water Quality Sampling and Analysis Plan, Revision 1, Santa Susana Field Laboratory, Ventura County, California. December. MWH, 2009. Draft Site-Wide Groundwater Remedial Investigation Report, Santa Susana Field Laboratory, Ventura County, California. Volumes 1 through 7. In Association with the SSFL Groundwater Advisory Panel, University of Guelph, Haley & Aldrich and AquaResource Inc. December. MWH, 2013. Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (Appendix D of Comprehensive Data Quality Objectives, CH2M HILL, 2013). March 5. MWH, 2014a. Report on Annual Groundwater Monitoring, 2013, Santa Susana Field Laboratory, Ventura County, California. January 3. MWH, 2014b. Final Development of Risk Based Screening Levels for Additional Groundwater Constituents, and Screening Level Clarifications at the Santa Susana Field Laboratory, Santa Susana, California. May 16. MWH, 2014c. Groundwater Monitoring Progress Report, First Quarter 2014, Revision 1, Santa Susana Field Laboratory, Ventura County, CA. June 16. MWH, 2014d. Draft Development of Risk Based Screening Levels for Additional Groundwater Constituents Detected at the Santa Susana Field Laboratory, Santa Susana, California. November 11. MWH, 2014e. Groundwater Monitoring Progress Report, Third Quarter 2014, Santa Susana Field Laboratory, Ventura County, CA. November 21. MWH, 2015. Report on Annual Groundwater Monitoring, 2014, Santa Susana Field Laboratory, Ventura County, California. February 20. URS, 2012. Chemical Soil Background Study Report, Santa Susana Field Laboratory, Ventura County, California. December. C-15 FIGURES Area within known No rocket engine or equipment testing DNAPL release? Compare available soil, soil vapor and rock core chemical sampling results to background (BTVs) or groundwater comparison values (GCVs) Are concentrations > BTVs or GCVs? No Yes Yes Deep boring results available? No List chemicals with concentrations > BTVs or GCVs Yes Yes Drill deep boring & analyze vadose zone & groundwater samples DTSC professional judgment requires deep boring? No See Tables C-1 and C-ES-1 Install well No Conditional no further action for vadose zone mass flux to groundwater Monitoring well along flow path nearby? Yes See Table Collect and analyze samples C-ES-1 No Recent groundwater sampling results available (within last 3 years)? Yes Yes Groundwater concentration >GCV? No Model future transport in accordance with vadose zone to groundwater mass flux TM Vadose Zone CMS Recommendations for Protection of Groundwater Methodology (Figure C-2) See Table C-3 Yes Model predicts leachate at water table >GCVs within next 50 years? See Tables C-2 and C-3 No SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA VADOSE ZONE TO GROUNDWATER EVALUATION METHODOLOGY FIGURE C-1 Step 1 – Obtain List of Chemicals Obtain list of chemicals exceeded their respective screening levels in both the vadose zone and groundwater samples during the Vadose Zone and Groundwater Data Evaluations and chemicals with EMLCs greater than their respective GCVs during the Transport Modeling Evaluation Step 2 – Determine HVZC Does chemical have a DTSC established BTV? Yes Load vertical concentration profile (alluvial with the BTV and run model Do background concentrations generate leachate greater than its comparison value? Yes No No Does concentration at lowest MDL or lowest reported result if lower than the lowest MDL generates leachate above the groundwater No comparison value? Load the alluvium and colluvium layer with the maximum reported concentration and re-run model Iterate transport model runs to identify the highest concentration that can remain in the vadose zone (HVZC) without generating leachate at a concentration above the leachate comparison value (LCV) Yes Modeled leachate exceed the leachate generated by BTV? No Step 3- Identify Sample Locations Exceeding HVZC Yes Identify vadose zone sample locations detected above the lowest MDL or lowest reported result Step 4 – Identify Vadose Zone CMS Areas Identify vadose zone sample locations with concentrations above HVZC Map locations with exceedances as vadose zone CMS area protective of groundwater Abbreviations: BTV background threshold value CMS corrective measures study CNFA conditional no further action DTSC Department of Toxic Substances Control HVZC highest vadose zone concentration that can remain without producing leachate at concentrations above the groundwater comparison value GCV groundwater comparison value LCV leachate comparison values. LCV equals GCV for chemicals with no DTSC established BTV and higher value between GCV and modeled leachate concentration generated by BTV loaded to vertical concentration file for chemicals where DTSC established BTV is available MDL method detection limit Recommended chemical for CNFA SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA VADOSE ZONE CMS RECOMMENDATIONS FOR PROTECTION OF GROUNDWATER METHODOLOGY FIGURE C-2 !< ( ! ( ! !< ( PZ-106 ! * # * # < ! < ! GCV) (VZ concentration > HVZC) Table C-1 Table C-2 Table C-3 ND ND ND O ND ND ND O ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND O ND O ND ND ND ND ND ND ND ND ND ND O ND ND ND ND ND ND ND O ND O O ND ND ND ND ND O ND O O ND ND ND ND O ND ND O ND ND ND O ND ND ND ND ND ND X X Yes ND O ND ND O O ND ND ND ND ND ND ND ND ND ND ND ND X O No O O ND O X O No ND ND ND ND ND ND ND ND ND ND ND ND Page 1 of 3 Recommendation NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA CMS NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA DRAFT TABLE C-ES-1 VADOSE ZONE TO GROUNDWATER EVALUATION EXECUTIVE SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Chemical Use Area Cluster: Chemicals Evaluated Chemical Group PAHs (a) Energetics TPH (b) PCBs Herbicides Pesticides Dioxins/Furans (c) Chemical 1-Methyl naphthalene 2-Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene (1) Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Fluoranthene Fluorene Indeno(1,2,3-cd)pyrene Naphthalene Phenanthrene Pyrene 2,4,6-Trinitrotoluene HMX Perchlorate RDX Diesel Range Organics (C12-C14) Diesel Range Organics (C14-C20) Diesel Range Organics (C15-C20) Diesel Range Organics (C20-C30) Diesel Range Organics (C21-C30) Gasoline Range Organics (C8-C11) Kerosene Range Organics (C11-C14) Oil Range Organics (C30-C40) Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1254 Aroclor 1260 2,4,5-T 2,4-Dichlorophenoxyacetic Acid (2,4-D) 2,4-Dichlorophenoxybutyric acid Dalapon Dicamba Dichloroprop Dinoseb MCPA MCPP Silvex 4,4'-DDD 4,4'-DDE 4,4'-DDT Aldrin alpha-BHC beta-BHC Chlordane delta-BHC Dieldrin Endosulfan I Endosulfan II Endosulfan sulfate Endrin Endrin aldehyde Endrin ketone gamma-BHC Heptachlor Heptachlor epoxide Mirex p,p'-Methoxychlor Toxaphene 1,2,3,4,6,7,8-Heptachlorodibenzofuran 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin 1,2,3,4,7,8,9-Heptachlorodibenzofuran 1,2,3,4,7,8-Hexachlorodibenzofuran 1,2,3,4,7,8-Hexachlorodibenzo-p-dioxin 1,2,3,6,7,8-Hexachlorodibenzofuran 1,2,3,6,7,8-Hexachlorodibenzo-p-dioxin 1,2,3,7,8,9-Hexachlorodibenzofuran 1,2,3,7,8,9-Hexachlorodibenzo-p-dioxin 1,2,3,7,8-Pentachlorodibenzofuran 1,2,3,7,8-Pentachlorodibenzo-p-dioxin 2,3,4,6,7,8-Hexachlorodibenzofuran 2,3,4,7,8-Pentachlorodibenzofuran 2,3,7,8-Tetrachlorodibenzo-p-dioxin 2,3,7,8-Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo-p-dioxin DioxinFuran_TEQ_Mammal DioxinFuran_TEQ_Fish DioxinFuran_TEQ_Bird See last page for notes and abbreviations. EEL CC-01 Vadose Zone to Groundwater Evaluation Vadose Zone Data Groundwater Transport Model Evaluation Chemicals Identified for for data Chemicals in VZ Further Evaluation for Soil Rock Soil collected in Predicted to Reach Vapor Core Protection of GW 2010 - 2014 GW (EMLC > GCV) (VZ concentration > HVZC) Table C-1 Table C-2 Table C-3 O X ND No No X ND No X ND No X ND No X ND No X ND No X ND X X X X X X X X X X ND ND X ND ND ND X ND X O ND X ND ND ND ND ND X X ND ND X ND ND ND ND X ND X X O X ND ND X ND ND ND X ND X X X ND ND X X X ND ND X X X X X X X X X X X X X X X X X O O O ND ND ND ND O ND ND O ND O No No No No No No No No No No O Yes Yes No X O No ND ND No No ND Yes Yes ND Yes Yes ND ND No No ND No ND Yes ND No ND ND ND No No No ND ND ND Yes Yes No O O O O O O O O O O O O O O O O O No No No No No No No No No No No No No No No No No Page 2 of 3 Yes Yes Yes Recommendation NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA CMS NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA CMS NFA NFA NFA NFA CMS NFA NFA NFA NFA NFA NFA NFA CMS NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA CMS CMS NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA DRAFT TABLE C-ES-1 VADOSE ZONE TO GROUNDWATER EVALUATION EXECUTIVE SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Chemical Use Area Cluster: Chemicals Evaluated Chemical Group Metals Inorganics Chemical Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Calcium Chromium Cobalt Copper Hexavalent Chromium Iron Lead Lithium Magnesium Manganese Mercury Molybdenum Nickel Phosphorus Potassium Selenium Silver Sodium Strontium Thallium Tin Titanium Total Phosphorus Vanadium Zinc Zirconium Chloride Cyanides Fluoride Nitrate-N Nitrate-NO3 Phosphate Sulfate EEL CC-01 Vadose Zone to Groundwater Evaluation Vadose Zone Data Groundwater Transport Model Evaluation Chemicals Identified for for data Chemicals in VZ Further Evaluation for Soil Rock Soil collected in Predicted to Reach Vapor Core Protection of GW 2010 - 2014 GW (EMLC > GCV) (VZ concentration > HVZC) Table C-1 Table C-2 Table C-3 O X O No No X O Yes No X O No X O O X X No X O O O X No X ND O O O O X X No Yes No X ND O O O O O X O Yes No Yes Yes X O O O O O O O O O O ND X O Yes No O X O Yes Yes O O Recommendation NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA CMS NFA NFA Notes and Abbreviations (a) - In groundwater, the seven generally recognized carcinogenic PAHs (Benzo(a)anthracene, Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Chrysene, Dibenzo(a,h)anthracene, and Indeno(1,2,3-cd)pyrene) are screened by comparing the calculated Benzo(a)pyrene TEQ values against the Benzo(a)pyrene screening value. (b) - In groundwater, TPH analyses falling under the typical GRO (C6-C12), DRO (C13-C30), and ORO (C30-C40) carbon ranges are evaluated together for comparison against vadose zone GRO, DRO, and ORO analyses, as the carbon ranges analyzed in the vadose zone and in groundwater do not match up in many cases. (c) - In groundwater, dioxins and furans are screened by comparing the calculated 2,3,7,8-TCDD TEQ values against the 2,3,7,8-TCDD screening value. (1) - There is no groundwater screening level established for benzo(ghi)perylene - this chemical is a potential human health concern, but no toxicity criterion is available for it. EMLC - Estimated Maximum Leachate Concentration GCV - Groundwater Comparison Value GW - Groundwater HVZC - Highest Vadoze Zone Concentration VZ - Vadose Zone Blank cells indicate no data available or not evaluated X - chemical exceeded its respective screening level O - chemical detected ND - chemical not detected NFA - chemical is recommended for No Further Action in the vadose zone CMS - chemical recommended for Corrective Measures Study in the vadose zone See last page for notes and abbreviations. Page 3 of 3 DRAFT TABLE C-1 VADOSE ZONE AND GROUNDWATER DATA EVALUATION SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Vadose Zone Evaluation Chemical Use Area Cluster Groundwater Evaluation Chemicals Exceeded BTVs or GCVs in Vadose Zone Samples Soil Soil Rock Vapor Core Wells Selected for Comparison Wells Considered in Analysis ES-23, potentially intercepts flow from the northeastern portion of EEL CC-01 under the pumping condition, within Compound A CC-01 1 SVOCs: bis(2-Ethylhexyl)phthalate, Di-n-octyl phthalate PAHs: 2-Methylnaphthalene, Acenaphthene, Acenaphthylene, Anthracene, Benzo(a)anthracene, Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(ghi)perylene1, Benzo(k)fluoranthene, Chrysene, Dibenzo(a,h)anthracene, Fluoranthene, Fluorene, Indeno(1,2,3-cd)pyrene, Naphthalene, Phenanthrene, Pyrene Energetics: Perchlorate TPHs: DRO: C15-C20, C21-C30, ORO: C30-C40 PCBs: Aroclor 1254, Aroclor 1260 Herbicides: 2,4-Dichlorophenoxybutyric Acid, MCPA, VOCs: Silvex N/A TCE Pesticides: 4,4'-DDD, 4,4'-DDT, beta-BHC, Endosulfan I, Endosulfan sulfate, Endrin, Endrin aldehyde, Heptachlor, Heptachlor epoxide, Mirex Dioxins/Furans: 1,2,3,4,6,7,8-HpCDD, 1,2,3,4,6,7,8HpCDF, 1,2,3,4,7,8,9-HpCDF, 1,2,3,4,7,8-HxCDD, 1,2,3,4,7,8-HxCDF, 1,2,3,6,7,8-HxCDD, 1,2,3,6,7,8HxCDF, 1,2,3,7,8,9-HxCDD, 1,2,3,7,8,9-HxCDF, 1,2,3,7,8-PeCDD, 1,2,3,7,8-PeCDF, 2,3,4,6,7,8-HxCDF, 2,3,4,7,8-PeCDF, 2,3,7,8-TCDD, 2,3,7,8-TCDF, OCDD, OCDF Metals: Sb, As, Ba, Be, Ca 2, Cd, Cr VI, Mn, Hg, Ag, Na Inorganics: Fluoride, Nitrate-NO3 GW Sample Collection Dates ES-28 No recent pertinent data ES-29 2010-2013: VOCs 2014: 1/31, 7/23 ES-30 2010: 2/10 2013: 7/22 2014: 1/31, 7/23 PZ-038 No recent data available Chemicals Exceeded BTVs or GCVs in Vadose Zone Samples But Did Not Exceeded GCVs in Groundwater Samples Chemicals Exceeded BTVs or GCVs in Vadose Zone Samples and Exceeded GCVs in Groundwater Samples ES-26, intercepts flow under the pumping condition, within STL-IV and interpreted to be associated with STL-IV ES-28, intercepts flow from northeastern portion of EEL CC01, within Compound A CC-01 ES-29, ES-30, potentially intercepts flow from the northeastern portion of EEL CC-01 under the pumping condition, within Compound A CC-01 PZ-050, within EEL and recent data available PZ-038, intercepts flow under the pumping condition, insufficient water to sample and within Compound A CC-04 PZ-050 2014: 4/28, 4/29 PZ-039, no recent data, casing melted shut, within Compound A CC-04 PZ-036, RD-55A/B, intercepts flow under non-pumping condition downgradient of EEL, within STL-IV CC-03 and interpreted to be associated with STL-IV RS-15, potentially intercepts flow from northeastern portion of cluster under the pumping condition, within Compound A CC-01 RS-17 2011: 1/13 dry since 2011 RS-15 2011: 1/13, 1/17 dry since 2011 RS-37 2014: 2/13, 7/24, 10/13 SVOCs: bis(2-Ethylhexyl)phthalate, Di-n-octyl phthalate PAHs: 2-Methylnaphthalene, Acenaphthene, Acenaphthylene, Anthracene, Benzo(a)pyrene TEQ (a), Naphthalene, Fluoranthene, Fluorene, Phenanthrene, Pyrene Energetics: Perchlorate VOCs: TCE TPHs(b): ORO: C30-C40 TPH: DRO: C21-C30 PCBs: Aroclor 1254, Aroclor 1260 Herbicides: 2,4-Dichlorophenoxybutyric Acid, MCPA, Metals: Cd (total and dissolved), Mn (total) Silvex Pesticides: 4,4'-DDD, 4,4'-DDT, beta-BHC, Endosulfan I, Endosulfan sulfate, Endrin, Endrin aldehyde, Heptachlor, Heptachlor epoxide, Mirex Dioxins/Furans: 2,3,7,8-TCDD TEQ (c) Metals: Sb, As, Ba, Be, Cr VI, Hg, Ag, Na Inorganics: Fluoride, Nitrate-NO3 RS-17, within EEL CC-01 RS-37, new well installed in EEL CC-01 in December 2013 for replacement of RS-17 Notes and Abbreviations 1 - There is no GCV established for Benzo(ghi)perylene - this chemical is a potential human health concern but no toxicity criterion is available for it. 2 - There is no GCV established for calcium - this chemical is not recognized as a human health concern. (a) - In groundwater, the seven generally recognized carcinogenic PAHs (Benzo(a)anthracene, Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Chrysene, Dibenzo(a,h)anthracene, and Indeno(1,23,-cd)anthracene are screened by comparing the calculated Benzo(a)pyrene TEQ values against the Benzo(a)pyrene screening value. (b) - In groundwater, TPH analyses falling under the typical GRO (C6-C12), DRO (C13-C30), and ORO (C30-C40) carbon ranges are evaluated together for comparison against vadose zone GRO, DRO, and ORO analyses. (c) - In groundwater, dioxins and furans are screened by comparing the calculated 2,3,7,8-TCDD TEQ values against the 2,3,7,8-TCDD screening value. See the last page for additional notes and abbreviations Page 1 of 2 DRAFT TABLE C-1 VADOSE ZONE AND GROUNDWATER DATA EVALUATION SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Notes and Abbreviations Continued BTVs - Background Comparison Values CC - Chemical Use Area Cluster DRO - Diesel Range Organics EEL - Environmental Effects Laboratory GRO - Gasoline Range Organics GCVs - Groundwater Comparison Values N/A - Not Applicable GW - Groundwater ORO - Oil Range Organics PAHs - Polycyclic Aromatic Hydrocarbons PCB - Polychlorinated Biphenyls Sb - Antimony As - Arsenic Ba - Barium Be - Beryllium Ca - Calcium Cd - Cadmium RCRA - Resource Conservation and Recovery Act RFI - RCRA Facility Investigation SVOCs - Semi-Volatile Organic Compounds TBD - To Be Determined TCE - Trichloroethene TPH - Total Petroleum Hydrocarbons VOCs - Volatile Organic Compounds MCPA - Methylchlorophenoxypropionic Acid DDD - Dichlorodiphenyldichloroethane DDT- Dichlorodiphenyltrichloroethane BHC - Benzene hexachlorocyclohexane HpCDD - Heptachlorodibenzo-p-dioxin HpCDF - Heptachlorodibenzofuran HxCDD - Hexachlorodibenzo-p-dioxin HxCDF - Hexachlorodibenzofuran PeCDD - Pentachlorodibenzo-p-dioxin PeCDF - Pentachlorodibenzofuran OCDD - Octachlorodibenzo-p-dioxin OCDF - Octachlorodibenzofuran TCDD - Tetrachlorodibenzo-p-dioxin TCDF - Tetrachlorodibenzofuran Cu - Copper Cr VI- Hexavalent Chromium Mn - Manganese Hg - Mercury Page 2 of 2 DRAFT TABLE C-2 VADOSE ZONE TO GROUNDWATER TRANSPORT MODELING RESULTS SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Chemical Group SVOCs PAHs Energetics PCBs Herbicides Pesticides Dioxins/ Furans TPHs Metals Inorganics Chemical bis(2-Ethylhexyl) phthalate Di-n-octyl phthalate 2-Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3-cd)pyrene Fluoranthene Fluorene Naphthalene Phenanthrene Pyrene Perchlorate Aroclor 1254 Aroclor 1260 2,4-DB MCPA Silvex 4,4'-DDD 4,4'-DDT beta-BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex 1,2,3,4,6,7,8-HpCDD 1,2,3,4,6,7,8-HpCDF 1,2,3,4,7,8,9-HpCDF 1,2,3,4,7,8-HxCDD 1,2,3,4,7,8-HxCDF 1,2,3,6,7,8-HxCDD 1,2,3,6,7,8-HxCDF 1,2,3,7,8,9-HxCDD 1,2,3,7,8,9-HxCDF 1,2,3,7,8-PeCDD 1,2,3,7,8-PeCDF 2,3,4,6,7,8-HxCDF 2,3,4,7,8-PeCDF 2,3,7,8-TCDD 2,3,7,8-TCDF OCDD OCDF ORO (C30-C40 aliphatics) ORO (C30-C40 aromatics) ORO (C30-C40 median) Antimony Arsenic Barium Beryllium Hexavalent Chromium Mercury Silver Sodium Fluoride Nitrate-NO3 See last page for notes and abbreviations. Maximum Vadose Zone Reported Concentration* (mg/kg) 0.0503 0.099 0.012 0.017 0.0021 0.13 1.2 0.74 1 0.52 1.5 0.096 0.26 2.3 0.015 0.0022 0.91 2.5 0.043 0.099 0.046 3.2E-02 9.4E-01 1.4E-03 0.0018 0.019 7.3E-04 5.5E-04 5.5E-04 0.0005 0.0011 5.8E-04 4.7E-04 4.7E-03 1.5E-03 1.8E-04 1.6E-05 1.9E-05 7.0E-06 6.2E-05 7.7E-06 4.2E-05 1.8E-06 9.8E-06 1.0E-05 1.1E-05 2.8E-06 1.1E-06 2.3E-06 0.0428 6.4E-04 2600 2600 2600 7.5 110 230 1.9 3.2 0.033 3.5 1170 11.2 46 Vadose Zone Comparison Value GCV (mg/kg) 0.028 0.00637 0.0018 0.0018 0.000815 0.000645 0.001222 0.00164 0.003264 0.00353 0.002457 0.00102 0.000792 0.002466 0.001805 0.0017 0.001864 0.002586 0.000649 --0.027 0.398 0.000322 0.000186 0.006101 0.000126 0.0000826 0.000178 0.000159 0.00037 0.000116 0.00011 0.000279 2.41E-06 6.94E-07 6.55E-08 7.61E-08 1.25E-07 7.39E-07 1.69E-07 9.95E-07 9.84E-07 1.00E-07 1.64E-07 1.81E-07 2.18E-07 2.76E-08 2.81E-07 1.67E-05 1.19E-06 ---0.497 24.2 203.8 1.424 1.129 0.028 0.095 754 5.387 -- (ug/L) 4 500 50 380 380 3800 -0.2 -----250 250 17 3800 380 6 0.5 0.5 100 6.3 50 0.62 0.44 0.03 75 75 2 3.8 0.01 0.01 0.01 -------------3.00E-05 ---7.40E+02 7.40E+02 7.40E+02 2.5 7.7 150 0.14 14 0.06 0.17 190000 800 45000 Calculated Metal Kd (Note 1) (L/kg) ------------------------------------------------------879 785 213 892 1050 70 247 5 14.3 10.35 Koc Value (L/kg) 1.51E+07 8.32E+07 4.32E+03 7.08E+03 2.76E+03 2.95E+04 3.98E+05 1.02E+06 1.23E+06 1.23E+06 3.98E+05 3.80E+06 3.47E+06 1.07E+05 1.38E+04 2.00E+03 2.29E+04 1.05E+05 6.76E+00 7.60E+05 5.37E+06 1.85E+02 5.18E+01 2.60E+03 1.02E+05 2.63E+05 3.08E+03 1.60E+03 3.44E+03 1.14E+04 8.49E+03 2.30E+04 1.57E+04 7.10E+07 6.30E+07 7.90E+07 2.50E+07 2.50E+07 2.50E+07 2.30E+07 1.30E+07 2.30E+07 1.56E+07 3.37E+06 4.73E+06 2.30E+07 2.45E+06 4.84E+06 9.92E+05 7.90E+07 9.40E+07 7.94E+09 1.25E+05 3.16E+07 ----------- Calculated Organic Kd (Note 1) (L/kg) 3.47E+03 1.91E+04 9.94E-01 1.63E+00 6.35E-01 6.79E+00 9.15E+01 2.35E+02 2.83E+02 2.83E+02 9.15E+01 8.74E+02 7.98E+02 2.46E+01 3.17E+00 4.60E-01 5.27E+00 2.42E+01 1.55E-03 1.75E+02 1.24E+03 4.26E-02 1.19E-02 5.98E-01 2.35E+01 6.05E+01 7.08E-01 3.68E-01 7.91E-01 2.62E+00 1.95E+00 5.29E+00 3.61E+00 1.63E+04 1.45E+04 1.82E+04 5.75E+03 5.75E+03 5.75E+03 5.29E+03 2.99E+03 5.29E+03 3.59E+03 7.75E+02 1.09E+03 5.29E+03 5.64E+02 1.11E+03 2.28E+02 1.82E+04 2.16E+04 1.83E+06 2.88E+01 7.27E+03 ----------- EMLC (Note 2) (ug/L) 0 0 14 8.233 4.677 2.707 0 0 0 0 0 0 0 6.97E-04 3.828 5.648 67 6.87E-04 845 0 0 378.3 43280 3.741 1.00E-08 0 1.4 2.4 1.583 0.4866 0.9248 0.1082 0.2594 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.00001414 0 0 0 998 0 0 0.425 0.4004 477,200 1,691 1,728,000 ------- EMLC Value Greater Than GCV? (Yes/No) No No No No No No EMLC Value Greater Than 10 x GCV? (Yes/No) No No No No No No 0 No No --------------------- No No No No No Yes, 0-50 year No No Yes, 0-50 year Yes, 0-50 year No No No Yes, 0-50 year No No No No Yes, 0-50 year Yes, 0-50 year No No No No No No No No No No Yes No No No No No No No No No No No 0 No No No No No No No Yes, 0-50 year No No Yes, 0-50 year Yes, 0-50 year Yes, 0-50 year Yes, 0-50 year Yes, 0-50 year No No No No No No No No No No No No Yes EMLC TEF for PAHs (Notes 3,4) Page 1 of 2 Approximate Breakthrough Year (Note 5) Predicted Trend in Groundwater After Breakthrough to 100 years (Note 5) 1 Peaks at ~year 2, then decreases rapidly to below GCV at ~year 4 1 1 Peaks at ~year 3, then decreases rapidly to below GCV at ~year 4 Peaks at ~year 2, then decreases rapidly to below GCV at ~year 6 3 Peaks at ~year 22, then decreases to below GCV at ~year 48 16 11 Increasing Increasing 31 Peaks at ~year 32, then remains constant 10 37 1 1 2 Peaks at ~year 10, then remains constant Peaks at ~year 37, then remains constant Increasing Remains constant Peaks at ~year 2, then decreases Recommendation NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA Protection of GW Evaluation NFA NFA Protection of GW Evaluation Protection of GW Evaluation NFA NFA NFA Protection of GW Evaluation NFA NFA NFA NFA Protection of GW Evaluation Protection of GW Evaluation NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA NFA Protection of GW Evaluation NFA NFA Protection of GW Evaluation Protection of GW Evaluation Protection of GW Evaluation Protection of GW Evaluation Protection of GW Evaluation DRAFT TABLE C-2 VADOSE ZONE TO GROUNDWATER TRANSPORT MODELING RESULTS SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Chemical Group Chemical Maximum Vadose Zone Reported Concentration* (mg/kg) Vadose Zone Comparison Value GCV (mg/kg) (ug/L) Calculated Metal Kd (Note 1) (L/kg) Koc Value (L/kg) Calculated Organic Kd (Note 1) (L/kg) EMLC (Note 2) EMLC TEF for PAHs (Notes 3,4) (ug/L) EMLC Value Greater Than GCV? (Yes/No) EMLC Value Greater Than 10 x GCV? (Yes/No) Approximate Breakthrough Year (Note 5) Predicted Trend in Groundwater After Breakthrough to 100 years (Note 5) Recommendation Notes and Abbreviations No Recommended for NFA. Model predicts chemical will not exceed its applicable GCV at any time during the 100 year simulation. Recommended for Protection of GW Evaluation. Model predicts chemical will exceed its applicable GCV at some point during simulation years 0-50 and will either decrease to a concentration below the GCV at or prior to simulation year 50 or remain above the GCV for some or all of Yes, 0-50 year simulation years 51-100. * Maximum concentration reported in a rock core sample; the rock core concentration (Cr) was converted to an equivalent soil concentration (Ces) using the following equation: Ces = Kd x Cr 1 Metal Kds calculated from total and SPLP metals data reported by Ogden (1997) and other information sources. Organic chemical Kds calculated based on Koc x foc. 2 Modeling simulation based on utilizing the following range of profiles developed and groundwater recharge values: EEL Profile CC-01 Alluvial/Colluvial [feet] 6.56 Weathered Sandstone [feet] 6.23 Unweathered Sandstone [feet] Vadose Zone Transport Column [feet] 12.79 Groundwater Runoff Recharge Rate [inch/year] 2.87 3 For seven carcinogenic PAHs, predicted EMLCs were converted to a PAHs TEF value using the following equation, and then screened against the Benzo(a)pyrene GCV. PAHs TEF = (0.1 x benzo(a)anthracene EMLC) + (1.0 x benzo(a)pyrene EMLC) + (0.1 x benzo(b)fluoranthene EMLC) + (0.1 x benzo(k)fluoranthene EMLC) + (0.01 x chrysene EMLC) + (0.34 x dibenzo(a,h)anthracene EMLC) + (0.1 x indeno(1,2,3-cd)pyrene EMLC) For 17 dioxins and furans, predicted EMLCs were converted to a TEF value using the following equation, and then screened against the 2,3,7,8-TCDD GCV. 4 Dioxins/Furans TEF = (0.01 x 1,2,3,4,6,7,8-HpCDD EMLC) + (0.01 x 1,2,3,4,6,7,8-HpCDF EMLC) + (0.01 x 1,2,3,4,7,8,9-HpCDF EMLC) + (0.1 x 1,2,3,4,7,8-HxCDD EMLC) + (0.1 x 1,2,3,4,7,8-HxCDF EMLC) + (0.1 x 1,2,3,6,7,8-HxCDD EMLC) + (0.1 x 1,2,3,6,7,8-HxCDF EMLC) + (0.1 x 1,2,3,7,8,9-HxCDD EMLC) + (0.1 x 1,2,3,7,8,9-HxCDF EMLC) + (1.0 x 1,2,3,7,8-PeCDD EMLC) + (0.03 x 1,2,3,7,8-PeCDF EMLC) + (0.1 x 2,3,4,6,7,8-HxCDF EMLC) + (0.3 x 2,3,4,7,8-PeCDF EMLC) + (1.0 x 2,3,7,8-TCDD EMLC) + (0.1 x 2,3,7,8-TCDF EMLC) + (0.0003 x OCDD EMLC) + (0.0003 x OCDF EMLC) 5 6 7 ~ -CMS EMLC foc GCV in/yr Kd Koc KRO L/Kg Evaluated if predicted EMLC value greater than its applicable GCV. Liquid phase biodegradation rate was not applied. Henry's Law Constant, air and water diffusion coefficient was applied on all chemicals except for metals. Approximately Not applicable Corrective Measures Study Estimated Maximum Leachate Concentration Organic carbon fraction in soil; a value of 0.00023 used for Organic Kd calculations Groundwater Comparison Value inch per year Soil-water partition coefficient Organic-carbon partition coefficient Kerosene range organics Liter per kilogram See last page for notes and abbreviations. mg/kg NFA PAHs PCBs SPLP TEF TPHs ug/L VOCs milligrams per kilogram No Further Action Polycyclic Aromatic Hydrocarbons Polychlorinated Biphenyl Synthetic Precipitation Leaching Procedure Toxic equivalency factor Total Petroleum Hydrocarbons micrograms per liter Volatile Organic Compounds Page 2 of 2 HpCDD HpCDF HxCDD HxCDF PeCDD PeCDF OCDD OCDF TCDD TCDF Heptachlorodibenzo-p-dioxin Heptachlorodibenzofuran Hexachlorodibenzo-p-dioxin Hexachlorodibenzofuran Pentachlorodibenzo-p-dioxin Pentachlorodibenzofuran Octachlorodibenzo-p-dioxin Octachlorodibenzofuran Tetrachlorodibenzo-p-dioxin Tetrachlorodibenzofuran DRAFT TABLE C-3 PROTECTION OF GROUNDWATER TRANSPORT MODELING RESULTS SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Screening Levels Chemical Use Area Cluster Chemical Group VOC Chemical Trichloroethene Energetic Perchlorate BTV (mg/kg) -- 6.49E-04 GCV (ug/L) 5 6 DRO (C21-C30 Aromatics) -- 100 2,4-DB 0.03 100 MCPA 0.398 6.3 1.26E-04 0.025 1.16E-04 0.01 1.10E-04 0.01 203.8 150 Herbicides beta-BHC Pesticides Heptachlor Heptachlor epoxide Barium Cadmium 0.0052b Trial 1 0.0001 Trial 2 0.0002 3.33 Trial 3 BTV Max Trial 1 0.0003 6.5E-04 0.043 6.6E-04 5 21 1,421 22 Max 0.435 HVZC2 Groundwater Soil (mg/kg) Soil Vapor3 (ug/L) Exceeded GCV in Groundwater Samples Collected in 2010-2014 -- -- 1.67 5 0.0003 1.35 Yes CMS - ELSV01, ELSV02, ELSV03 21 6.5E-04 -- No CMS - ELBS2001, ELBS2007, ELBS2020, ELBS2022, SL143-SA5C4 100 900 -- Yes NFA - no location exceeded HVZC. Groundwater sample results are evaluated further in the Groundwater Source Zone and Plume Characterization evaluation (Appendix D) 571 0.027 -- No CMS - ELBS2009 12,950 0.398 -- No CMS - ELBS2000, SL-143-SA5C4 0.30 1.3E-04 -- No CMS - ELBS2000 0.02 1.2E-04 -- No CMS - ELBS2000 0.06 1.1E-04 -- No CMS - ELBS2009 998 230 -- No NFA - no location exceeded HVZC Yes NFA - no location exceeded HVZC. Groundwater sample result with concentration above comparison value not verified. Groundwater results are evaluated further in Appendix D. 0 900 -- 1.4E-05 0 BTV Max Trial 1 BTV Max Trial 1 BTV Max Trial 1 BTV Max Trial 1 BTV Max Trial 1 BTV Max 0.027 0.032 0.028 0.398 0.94 0.399 1.3E-04 7.3E-04 1.4E-04 1.2E-04 5.8E-04 1.3E-04 1.1E-04 4.7E-04 1.2E-04 203.8 230 BTV 0.435 0.2 -- -- -- -- -- 203.8 571 676 592 12,950 30,610 12,990 0.30 1.94 0.37 0.02 0.12 0.03 0.06 0.26 0.07 998 998 0 0.435 0.20 Max 4.2 0 BTV 723 0 4.2 -- Metals Manganese Mercury See last page for notes and abbreviations. 723 0.028 150 0.063 723 Max 887 BTV Max 0.028 0.033 Recommendations - Vadose Zone Sampled Locations Recommended for CMS for Groundwater Protection LCV1 (ug/L) 86.7 Max DRO (C21-C30 Median) 1 Max Max DRO (C21-C30 Aliphatics) TPH Transport Model Trial Summary for HVZC A/C WS/UWS Concentration Input Input EMLC Input Type Concentration Concentration (ug/L) (mg/kg) (mg/kg) Max 446.7 0.0268a 150 887 -- Yes NFA - no location exceeded HVZC. Groundwater sample result with concentration above comparison value not verified. Groundwater results are evaluated further in Appendix D. 0.43 0.033 -- No NFA - no location exceeded HVZC 0 0.028 0.425 0.425 Page 1 of 2 DRAFT TABLE C-3 PROTECTION OF GROUNDWATER TRANSPORT MODELING RESULTS SUMMARY EEL RFI SITE, BOEING RFI SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CA Screening Levels Chemical Use Area Cluster Chemical Group Chemical Silver BTV (mg/kg) GCV (ug/L) 0.095 0.17 Metals Sodium 754 Transport Model Trial Summary for HVZC A/C WS/UWS Concentration Input Input EMLC Input Type Concentration Concentration (ug/L) (mg/kg) (mg/kg) BTV 0.400 0.095 0.095 Max 0.400 3.5 BTV 754 402,400 Max 1170 508,200 190000 754 Trial 1 755 402,400 Trial 2 756 402,700 BTV Max Lowest Level Max Trial 1 Trial 2 Trial 3 5.387 11.2 0.44 46 1.0 1.3 1.4 HVZC2 Groundwater Soil (mg/kg) Soil Vapor3 (ug/L) Exceeded GCV in Groundwater Samples Collected in 2010-2014 0.40 3.5 -- No NFA - no location exceeded HVZC 402,400 755 -- No NFA - Sodium was not identified as a chemical used historically at EEL and was not identified as a risk driver during the human health and ecological risk assessment. Sodium is naturally occurring and the sample with the detected concentration that exceeded the soil screening level and produced a leachate above the estimated background falls within the background range (upper simultaneous limit with 95% confidence (USL95)of 1,530 milligrams per kilogram, (URS, 2012). 1,691 11.2 -- No NFA - no location exceeded HVZC 45,000 1.3 -- No CMS - ELBS2035 1 Fluoride 5.387 800 -- 45,000 Inorganic Nitrate-NO3 5.387 -- 1,691 1,691 14,720 1,728,000 33,460 43,510 46,840 Recommendations - Vadose Zone Sampled Locations Recommended for CMS for Groundwater Protection LCV1 (ug/L) Notes and Abbreviations 1. LCV equals GCV for chemicals with no DTSC established BTV and higher value between GCV and modeled leachate concentration generated by background concentrations throughout the vadose zone profile for chemicals where DTSC established BTV is available. 2. HVZC - highest concentration that can remain in the vadose zone without generating leachate at concentration above the leachate comparison value. 3. Soil Vapor HVZC was estimated utilizing the three-phase partitioning equation in the Arizona Department of Environmental Quality, Soil Vapor Samping Guidance dated July 10, 2008 and revised May 19, 2011 (ADOE, 2011). 4. Sample SL-143-SAS5 was included based on a qualitative analysis performed on additional data collected at the EEL RFI site by the Department of Energy (Attachment C-5). a. Maximum TCE concentration (120 ug/L) reported in soil vapor was converted to soil equivalent concentration using the three-phase partitioning equation (ADOE, 2011). b. Maximum TCE concentration (224 ug/L) reported in rock core was converted to soil equivalent concentration using the following equation: Soil concentration [mg/kg] = Rock Core Concentration [ug/L] x Kd [L/Kg] x 0.001 [mg/ug] -A/C BTV CC CMS NFA EMLC GCV HVZC Kd Not applicable Alluvium/Colluvium Background Threshold Value Chemical Use Area Cluster Corrective Measures Study No Further Action Estimated Maximum Leachate Concentration Groundwater Comparison Value Highest Vadoze Zone Concentration Soil-water partition coefficient See last page for notes and abbreviations. LCV Max mg/L MDL NC SV ug/L VOCs VZ WS/UWS Page 2 of 2 Leachate Comparison Value Vadose zone maximum reported concentration milligrams per liter Method Detection Limit Not calculated Soil Vapor micrograms per liter Volatile Organics Vadose Zone Weathered Sandstone/Unweathered Sandstone DRAFT ATTACHMENTS ATTACHMENT C-1 ESTIMATE OF TRANSPORT DISTANCES BASED ON DARCY FLUX SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA ESTIMATE OF TRANSPORT DISTANCES BASED ON DARCY FLUX ATTACHMENT C-1 ATTACHMENT C-2 SESOIL TRANSPORT MODELING INPUTS AND ASSUMPTIONS TECHNICAL MEMORANDUM TO: Michael Bower, Boeing DATE: February 25, 2015 FROM: Geoffrey L. Upson, PhD. REFERENCE: 10506443 SUBJECT: Transport Modeling Inputs and Assumptions SESOIL assumes steady state flow conditions and is based on mass balance and partitioning of the chemical between the dissolved, sorbed, vapor, and pure phases. SESOIL contains five basic files for constructing a vadose zone transport modeling scenario; climate, chemical, soil, washload (not used in this modeling exercise), and application. Each file contains various sub-files with additional data inputs that are used to develop a unique and representative vadose transport column for each RFI site chemical use area (CUA) cluster (CC). The vadose zone transport column developed for each cluster represents a compilation of many data points and sets and reflects general conditions rather than a specific, unique location within the CC. Vadose Zone Transport Column The groundwater depth was obtained from available 2011 groundwater data for wells associated with the cluster. Groundwater depths were converted to groundwater elevations by considering the measuring point elevation of each well within the cluster for which measurements were available. In the case of multiple wells for a cluster, the median groundwater elevation for the cluster was calculated. In the event that there were an insufficient number of measurements to calculate the median groundwater elevation for a cluster, groundwater data from a longer timeframe, from 2010 through 2013, were used. If a significant change in groundwater elevation occurred in a well between 2010 and 2013, that well was excluded from the calculation of the median groundwater elevation. The median soil sample depth for the cluster was calculated from available sample locations and individual sample depths were estimated from soil thickness contour maps. The median soil (Alluvium/Colluvium [A/C]) thickness portion of the vertical profile is calculated from data provided in available soil and soil vapor boring logs for each cluster. Technical Memorandum Transport Modeling Inputs and Assumptions February 25, 2015 Page 2 The total profile thickness for a cluster was calculated by subtracting the median groundwater elevation (in feet msl) from the median sample elevation (in feet msl). The median soil (Alluvium/Colluvium [A/C]) portion of the profile was subtracted from the calculated total thickness of the vadose zone profile; the remaining profile was established as the thickness of the weathered sandstone/unweathered sandstone (WS/UWS) portion. The individual layers within the A/C and WS/UWS portions of the profile were based on the requirements listed in the Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (MWH, 2013; Appendix D of the DQO Report [CH2M HILL, 2013]) and available boring logs for each cluster. Typically, the calculated profiles are thick enough to warrant the use of four major layers consisting of 10 sublayers within each major layer. In the event of shallow groundwater depths, vadose zone transport profiles may contain only three major layers with 10 sublayers. The first two major layers are each 50 centimeters (cm) thick with layer #1 including a volatilization factor of 0.5, while layer #2 includes a volatilization factor of 0.25. Major layers #3 and #4 do not include volatilization factors (i.e., 0). Layers #3 and #4 will be either A/C or WS/UWS depending on the data obtained from available site soil boring logs. Chemical Properties The chemical and physical properties for each chemical modeled in this exercise represent median values. Because sources for chemical and physical properties of each chemical listed in the SESOIL chemical database are generally not identified, except occasionally in their chemical names (e.g., TCE (Trichloroethylene) R9, TCE (Trichloroethylene) Ohio EPA), extensive searches were conducted to identify the sources used in the SESOIL chemical database, as well as additional data sources (e.g. National Institute of Science and Technology database, various EPA databases) to document and calculate representative median chemical and physical property values for each chemical. These properties included water solubility, Henry’s Law constant, organic-carbon partition coefficient (Koc), soil-water partition coefficient (Kd), water and air diffusion coefficients, and molecular weight. Biodegradation rates were not used in the development of organic chemical profiles, thus providing a more conservative profile for these types of chemicals. The median values used for each chemical modeled are located in the SESOIL model output report on the “Profile and Load Report” page. Technical Memorandum Transport Modeling Inputs and Assumptions February 25, 2015 Page 3 Vertical Concentration Profile – Sublayer Load Vertical concentration profiles (sublayer loads) were developed based on the maximum concentrations detected and available sampling results from the vadose zone sampled locations for each chemical. Per the Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (MWH, 2013; Appendix D of the DQO Report [CH2M HILL, 2013]), the organic chemicals modeled in this exercise were assumed not to occur naturally in the subsurface environment, particularly in the WS/UWS portion of the profile. As a result, unless a sample was collected in the WS/UWS portion of the profile, organic chemical concentrations were assigned an initial (i.e., time “0”) value of 0 milligrams per kilogram (mg/kg), while inorganic chemicals were assigned their respective BTVs in the WS/UWS portion of the profile. Approaches for developing vertical concentration profiles are presented below: Borings with One Sample from the A/C Portion of the Profile If the maximum concentration was reported in a boring at a depth corresponding to the A/C portion of the profile and there were no shallower and deeper sample results available from the boring location, the reported inorganic or organic chemical concentration was applied to the entire A/C portion of the profile. In the WS/UWS portion of this one-sample profile, organic chemical concentrations were assigned a value of 0 mg/kg, while inorganic chemical concentrations were assigned as their respective BTVs. Borings with One Sample from the WS/UWS Portion of the Profile If the maximum concentration was reported in a boring at a depth corresponding to the WS/UWS portion of the profile and there were no shallower or deeper sample results available from the boring location, the reported inorganic or organic chemical concentration was applied to the entire A/C profile and down to the corresponding sampled depth of the WS/UWS portion of the profile. For the remainder portion of the WS/UWS profile, organic chemical concentrations were assigned a value of 0 mg/kg, while the inorganic chemical concentrations were assigned as their respective BTVs. Borings with Two or More Samples If the maximum concentration was reported in a boring where two or more sample results were available, a concentration curve was generated by subtracting the second highest concentration from the Technical Memorandum Transport Modeling Inputs and Assumptions February 25, 2015 Page 4 maximum concentration and dividing by the number of sublayers between the samples. The result yielded a change in concentration for each sublayer. Depending on whether the maximum concentration occurred in the shallowest/shallower or deepest/deeper sample in a boring, the concentration change per sublayer was either added to, or subtracted from the shallowest/shallower sample concentration. At sublayer intervals shallower than the first sample used in the concentration curve calculation, the chemical concentration reported in the first sample used in the concentration curve calculation was assigned. At sublayer intervals deeper than the second sample used in the concentration curve calculation that are still within the A/C portion of the profile, the chemical concentration of that sample was used to the interface of the A/C and WS/UWS portions of the profile. For the WS/UWS portion of the profile, 0 mg/kg or respective BTVs were assigned for organic and inorganic chemicals, respectively, unless the second sample was collected from the WS/UWS portion of the profile. In this latter case, organic chemical concentrations were assigned an initial (i.e., time “0”) value of 0 mg/kg, while the inorganic chemical concentrations were assigned as their respective BTVs for the remaining portion of the WS/UWS profile. Other Transport Modeling Inputs Other inputs required to conduct vadose zone transport modeling include groundwater recharge, climate, soil parameters, and the surface area of each CC. A range of groundwater recharge values for each CC were obtained from the calibrated groundwater flow model as presented in the Site-wide Groundwater Remedial Investigation Report (MWH, 2009). The Pierce College file in the SESOIL climate database was selected for RFI sites and their associated CCs and presented in the SESOIL model output report on the “Climate Report” page. Soil and sandstone parameter inputs necessary to complete profile development were derived from the range of values provided in Table 6 of the Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (MWH, 2013; Appendix D of the DQO Report [CH2M HILL, 2013]). The profile parameters consist of an average bulk density of 2.06 g/cm3 and an organic carbon fraction of 0.023 percent (%). The soil disconnected index (SDI), effective porosity (EP), and intrinsic permeability (IP) values were varied as necessary in the application file to achieve the range of estimated recharge from the flow model for each CC. Technical Memorandum Transport Modeling Inputs and Assumptions February 25, 2015 Page 5 The application file utilizes the calculated surface area of CC plus the thickness of each major layer in addition to an assigned IP value for each major layer. For A/C layers, the IP value was listed as 1.00x10-8 cm2, while the IP values for the WS/UWS major layers were varied as necessary to achieve the range of estimated recharge for each CC. The input values used for the soil and application files are shown on the “Profile and Load Report” page and hydrological cycle is presented on the “Hydrologic Cycle Report” page of the SESOIL model output report. Sensitivity Analysis Formal sensitivity analysis has not been conducted during this phase of the modeling exercise. However, the sensitivity of changes in the various inputs for the soil and application files was observed during model simulations to develop the hydrological cycle. Large numbers of SESOIL modeling runs conducted during the development of hydrological cycles for many chemical use area clusters in each RFI site show that changes in total vadose zone profile thickness and lithologic composition of the profile most significantly affect model output. Specifically, significant changes in the thicknesses of the alluvium/colluvium and weathered/unweathered sandstone portions of the vadose zone profile have a major influence on the estimated arrival and leachate concentration of any chemical. In addition, changing the soil disconnectedness index, effective porosity, and intrinsic permeability values to achieve the target hydrological cycle for a chemical use area cluster can also significantly impact model output. Where the vadose zone is thin [i.e., usually less than about 3.5 feet depending on lithology (e.g. alluvium, weathered sandstone)], application of the estimated recharge rates obtained from the threedimensional groundwater flow model affects estimated chemical arrival and leachate concentrations. However, this modeling effort is sufficiently conservative to ensure that potential future threats to groundwater by chemicals present in soil at the measured concentrations as reported in the characterization program will be evaluated in the CMS. Transport Modeling Output Files SESOIL results for each chemical modeled are shown in the “Pollutant Cycle Report” of the SESOIL model output report. Each Pollutant Cycle Report graphically displays the movement of a chemical through the profile to groundwater over a 100 year simulation timeframe. From 0 to 50 years, the modeling output approximates the time when discharge of a chemical may have occurred to the present (i.e., ~1965 to current). The 50 to 100 year timeframe approximates the predicted movement of a Technical Memorandum Transport Modeling Inputs and Assumptions February 25, 2015 Page 6 chemical from the present to 2055. The estimated maximum leachate concentration reported for each chemical and the timeframe when the EMLC occurs are also shown on the Pollutant Cycle Report. In addition, the distribution of each chemical into various profile compartments (e.g. adsorbed, in solution) is also reported. REFERENCES CH2M HILL, 2013. Comprehensive Data Quality Objectives, RCRA Field Investigation Santa Susana Field Laboratory, Ventura County, CA. March. MWH, 2009. Draft Site-Wide Groundwater Remedial Investigation Report, Santa Susana Field Laboratory, Ventura County, California. Volumes 1 through 7. In Association with the SSFL Groundwater Advisory Panel, University of Guelph, Haley & Aldrich and AquaResource Inc. December. ___, 2013. Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (Appendix D of Comprehensive Data Quality Objectives, CH2M HILL, 2013). March 5. ATTACHMENT C-3 MONITORING WELL RS-37 WELL CONSTRUCTION DIAGRAM, AND WELL DEVELOPMENT LOG FILE: SANTA DRILLING Expansion Cap\ Ground Surface jg?; 12? Casing Monumem? /wifh Locking Lid 3? 3? Concrete Pad Medium BenIoniIe Chips\ /liCemenI?Benfonife Grouf SeaI 4? 80 PVC Casing\' 4? 80 PVC Screen (0020? Slot) 18.42? Top of BenIonIIe SeaI ?10.6? Top of FiIIer Pack ?13.0? Top of Screen ?13.5? CenIraIizer /10.75? DIG. BorehoIe (Tricone) Mom?erey Lapis Lusfre Sand ?42.5? Cem?raIizer ?43.0? BoHom of Screen Medium BenIonIIe Chi ?50? BoHom of BorehoIe Io ScaIe MWH SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIOFRNIA DECEMBER 2013 MONITORING WELL RS-37 CONSTRUCTION DIAGRAM . Client: Total well depth 5; WC Min. Number Well Volumes to be Purged: Site: A Well Diameter Vol. per casing (gal): Well Number: Borehole Diameter [0 3'5. Vol. per borehole (gal): Job Number: (less casing and ?lter pack) I Gauging Date: Static water level ,4 W0 Amt. one well vol (gal): I 9 9 Development method: Bailer ID: Previous static water level I 2: . Z. I Total gal. to be urged: Purging method: Sample Date: Standing water column 2.3 . Sampling method: All measurements taken from: 1 Top of easing, Protective casing, Ground level 42/5 494,. Lei) . 7?5 - 25.15 2534?! MIL 26.2 PASI-IFO/Admin/Standard MW orms/GW Gauging and Sampling Log ATTACHMENT C-4 SUMMARY OF RADIOLOGICAL DATA EEL RFI SITE ATTACHMENT C-4 SUMMARY OF RADIOLOGICAL DATA EEL RFI SITE STRONTIUM-90 EXCEEDANCE An assessment of radiological data collected at the EEL RFI Site was performed with regard to the transport of contaminants from the vadose zone to groundwater evaluation. Radiological data collected at the EEL RFI Site were not included in the vadose zone to groundwater evaluation presented in the body of this Appendix C, as there is not a known source of radionuclides at this RFI site. The purpose of this assessment is to evaluate if the concentrations of radiological constituents in soil at the EEL RFI Site have potential to impact groundwater. A single soil/sediment sample (A3_SED_DG-14) contained strontium-90, (90Sr) at an activity of 0.275 picocuries per gram (pCi/g) slightly above its soil characterization level (SCL) of 0.24 pCi/g at the EEL RFI site. Soil/sediment samples collected around A3_SED_DG-14 did not indicate the presence of 90Sr concentrations above the SCL in surrounding soils. The causes for the presence of this radionuclide at a level slightly exceeding its SCL at EEL chemical use area cluster 1 (EEL CC 1) are unknown. No reference has been located documenting industrial processes using this particular radionuclide at the EEL RFI Site or at this particular chemical use area cluster. Therefore, it is more likely the presence of this radionuclide is due to historic global aerial deposition or results from local soil erosion and surface water transport from upslope areas. A qualitative modeling evaluation using available data from the literature was conducted regarding the likelihood of 90Sr to be transported to groundwater by recharge waters in the vicinity of the EEL CC 1 at an activity of concern [California and federal maximum contaminant level (MCL) for drinking water of 8 picocuries per liter (pCi/L)]. The results of this evaluation suggest it is very unlikely 90Sr will migrate to groundwater over a 100-year timeframe, thus it is recommended for no further action (NFA). This conclusion is based on the following: • • • • The reported activity of 90Sr and its infrequent occurrence in soil and sediment samples (one isolated detection above the SCL at the EEL RFI Site) suggests the sample location does not represent a source of any meaningful size or volume. The approximately 13-foot thick vadose zone consisting of seven feet of alluvium/colluvium and six-feet of unweathered bedrock will partition a significant portion of the 90Sr mass to the solid fraction of the profile using an accepted distribution coefficient (Kd) of 30 (Argonne National Laboratory, 2007). Reported 90Sr Kd values range from 10 to 57 liters per kilogram (L/kg) (various literature sources), while specifically for sandy and loamy soils, Kd values in the range of 22 to 57 L/kg, respectively, were reported by Gil-Garcia et al (2009). The Kd values referenced fall towards the lower end of the literature values reported for metals (MWH, 2014). The absence of 90Sr in groundwater beneath Area IV where soil/sediment sampling results report appreciably higher activities than that encountered at this location. Review of historical groundwater data shows there is only a single location where 90Sr has been reported in groundwater at a concentration above its 8 pCi/L drinking water MCL in Area IV at a historic radionuclide release associated with a former leach field (alluvium excavated in 1978) at the Radioactive Materials Handling Facility. REFERENCES: Argonne National Laboratory, 2007. Environmental Services Division, User’s Manual for RESRADOFFSITE, Version 2 (DOE/HS-0005). June. MWH, 2014. Technical Memorandum: Procedure for Calculating Inorganic Partition Coefficients for Application in Santa Susana Field Laboratory (SSFL) Vadose Zone Modeling. August 18. Gil-Garcia, C., A. Rigol and M. Vidal, 2009. New best estimates for radionuclide solid-liquid distribution coefficients in soils, Part 1: radiostrontium and radiocaesium. Journal of Environmental Radioactivity, 100 (690-696). ATTACHMENT C-5 ADDITIONAL DATA ASSESSMENT OF DEPARTMENT OF ENERGY DATA EEL RFI SITE ATTACHMENT C-5 ADDITIONAL DATA ASSESSMENT OF DEPARTMENT OF ENERGY DATA EEL RFI SITE An assessment of additional data collected at the EEL RFI Site by the Department of Energy (DOE) was performed with regard to the transport of contaminants from the vadose zone to groundwater evaluation. These data were provided to Boeing after the Data Summary and Findings Report (DSFR) for the EEL RFI site had commenced, and therefore evaluated in a qualitative nature only. The purpose of this assessment is to determine the potential impact the additional data have on the CMS boundaries or locations as defined during the vadose zone to groundwater evaluation for the EEL RFI Site presented in the body of this Appendix C. The additional DOE data were evaluated in the context of chemicals that were recommended for CMS in the vadose zone for protection of groundwater and whether concentrations of these chemicals in the additional data require modifications of the CMS boundaries or locations. Concentrations of chemicals that were recommended for CMS were screened against vadose zone screening values (background threshold values [BTVs], or groundwater comparison values [GCVs] if no BTV available), and those chemicals exceeding their vadose zone screening values were screened against the vadose zone concentrations protective of groundwater (highest vadose zone concentrations [HVZCs]) as determined by transport modeling conducted in the vadose zone to groundwater evaluation. The additional DOE data consisted of soil sample results collected from eight sample locations within the chemical use area cluster (CC) at the EEL RFI site (EEL CC 1). The data for these soil samples was reviewed for the following eight chemicals recommended for CMS in the vadose zone based on the vadose zone to groundwater evaluation: • Trichloroethene (TCE) • Perchlorate • 2,4- Dichlorophenoxybutyric Acid • Methylchlorophenoxypropionic Acid (MCPA) • Beta- Benzene hexachlorocyclohexane (BHC) • Heptachlor • Heptachlor epoxide • Nitrate-NO3 Of these chemicals, perchlorate and MCPA were detected at concentrations that exceeded their vadose zone screening values (BTVs) at sample location SL-143-SA5C. The HVZCs calculated for perchlorate and MCPA based on the modeling conducted in the vadose zone to groundwater evaluation were equivalent to the BTVs. As a result, the additional sample location with perchlorate and MCPA concentrations above their BTVs and HVZCs is recommended for CMS. Sample location SL-143-SA5C was not within an existing CMS area and was isolated from other perchlorate and MCPA exceedances and nearby data was not sufficient to delineate an area so it was added as a vadose zone CMS location for the EEL RFI Site. In summary, qualitative analysis of the DOE data as described above resulted in the addition of one vadose zone CMS location at sample SL-143-SA5C for perchlorate and MCPA. ATTACHMENT C-6 SESOIL TRANSPORT MODELING OUTPUT REPORT EEL RFI SITE SESOIL Hydrologic Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT 10.0 8.0 6.0 4.0 2.0 0.0 cm SUR. RUNOFF O ct No v De c Ja n Fe b M ar Ap r M ay Ju n Ju l Au g Se p NET INFILT. 7 .0 1 4 6 .0 1 2 5 .0 E G M M M 1 0 V A P O T R A N S R W . R U N O F F O IS . R E T E N O IS . B E L O W L 1 (% ) O IS . IN L 1 ( % ) cm 8 3 .0 6 Percent 4 .0 2 .0 4 1 .0 2 0 .0 O c t N o v D e c J a n F e b M a r A p r M a y J u n J u l A u g S e p - 1 .0 Units 0 Surface Water Runoff cm Inches Net Infiltration cm Inches Evapotranspiration cm Inches Soil Groundwater Soil Moisture Moisture Runoff Below Retention (Recharge) Layer 1 Layer 1 cm Inches cm Inches Percent Percent October November December January February March April May June July August September 0.63 2.34 1.28 1.77 2.36 1.74 0.31 0.28 0.01 0.00 0.36 0.27 0.25 0.92 0.50 0.70 0.93 0.69 0.12 0.11 0.00 0.00 0.14 0.11 0.74 3.92 4.14 6.61 6.10 5.64 2.29 0.21 0.05 0.01 0.12 0.39 0.29 1.54 1.63 2.60 2.40 2.22 0.90 0.08 0.02 0.00 0.05 0.15 0.90 2.61 2.56 3.17 4.21 4.45 2.49 0.64 0.39 0.37 0.44 0.73 0.35 1.03 1.01 1.25 1.66 1.75 0.98 0.25 0.15 0.15 0.17 0.29 0.08 0.68 0.27 0.36 -0.19 -0.18 -0.46 -0.31 -0.12 -0.08 -0.02 -0.03 0.03 0.27 0.11 0.14 -0.07 -0.07 -0.18 -0.12 -0.05 -0.03 -0.01 -0.01 -0.24 0.63 1.32 3.08 2.08 1.37 0.26 -0.11 -0.21 -0.29 -0.30 -0.31 -0.09 0.25 0.52 1.21 0.82 0.54 0.10 -0.04 -0.08 -0.11 -0.12 -0.12 Total 11.35 4.47 30.22 11.90 22.93 9.03 0.00 0.00 7.29 2.87 8.79 10.89 11.71 12.82 12.23 11.69 10.28 9.31 8.94 8.71 8.64 8.54 8.79 10.89 11.71 12.82 12.23 11.69 10.28 9.31 8.94 8.71 8.64 8.54 -- -- Climate Report Location Description: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Climatic Input File: Month Temperature o Units October November December January February March April May June July August September o C cm F 67.10 58.89 53.80 54.10 55.99 57.20 60.80 65.19 70.59 76.41 76.80 73.20 19.50 14.94 12.11 12.28 13.33 14.00 16.00 18.44 21.44 24.67 24.89 22.89 Evapotranspiration Rate Precipitation Total Inches cm 0.54 2.48 2.14 3.31 3.30 2.88 1.02 0.18 0.02 0.00 0.18 0.26 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 41.44 16.31 0.00 0.00 0 .9 3 0 .0 0 .8 2 5 .0 2 0 .0 2 4 .6274 .8 9 2 2 .8 9 2 1 .4 4 1 8 .4 4 1 9 .5 16 1 4 .9 4 134 1 3 .3 1 2 .1112 .2 8 1 5 .0 0 .7 2 5 0 .7 0 .6 6 5 0 .7 2 0 .7 2 0 .5 0 .5 0 .7 4 5 0 .7 6 0 .7 7 0 .7 7 5 0 .7 5 5 0 .6 8 5 0 .6 4 5 0 .6 5 0 .5 0 .5 0 .6 Fraction Temperature (degrees C) Albedo Humidity # per Length Fraction Fraction Fraction Month Days 0.55 0.250 0.725 0.130 0.350 1.77 0.200 0.665 0.420 0.400 2.50 0.200 0.645 0.500 0.410 3.50 0.200 0.650 0.570 0.500 3.11 0.200 0.685 0.470 0.450 3.55 0.200 0.720 0.360 0.500 1.88 0.320 0.500 0.200 0.720 0.20 0.250 0.745 0.070 0.450 0.09 0.250 0.760 0.040 0.400 0.09 0.250 0.770 0.010 0.300 0.13 0.250 0.775 0.040 0.250 0.41 0.250 0.755 0.070 0.250 Inches 1.372 6.299 5.436 8.407 8.382 7.315 2.591 0.457 0.051 0.010 0.457 0.660 Cloud Cover Storms 0 .5 0 .4 5 0 .4 0 .4 1 0 .0 C lo u d Cover H u m id ity 0 .4 5 0 .4 A lb e d o 0 .3 5 0 .3 0 .3 0 .2 5 5 .0 0 .2 0 .0 0 .2 5 0 .2 0 .2 0 .2 0 .2 0 .2 0 .2 5 0 .2 5 0 .2 5 0 .2 5 0 .2 ep 0 .0 Oct S l ug A Ju n ay Ju pr M A ar b M n Fe Ja ec D N O ct ov 0 .1 No v Dec Jan Feb M ar Ap r M ay Jun J ul Au g Sep 4 .0 9 .0 8 .4 0 7 8 .3 8 2 8 .0 3 .5 3 .5 5 3 .5 7 .3 1 5 7 .0 3 .1 1 3 .0 6 .2 9 9 6 .0 2 .5 2 .5 Storm Data 5 .4 3 6 5 .0 L e n g th cm M o n th ly 2 .0 P r e c ip E v a p o tr a n s 4 .0 Nu m ber o f S to r m s 1 .8 8 1 .7 7 1 .5 3 .0 2 .5 9 1 1 .0 2 .0 1 .3 7 2 0 .4 5 7 0 .0 0 O ct 0 No v 0 Dec 0 Jan 0 Feb 0 M ar 0 Apr 00 .0 5 1 0 M ay 0 .4 5 7 J un Jul 00 .0 1 Au g 0 0 .4 2 0 .4 1 0 .4 7 0 .6 6 0 Sep 0 .5 7 0 .5 5 0 .5 1 .0 0 .3 6 0 .3 2 0 .1 3 0 .0 Oct No v Dec Jan Feb M ar Apr M ay 0 .4 1 0 .2 0 .0 7 0 .1 3 0 0 .0 9 0 .0 7 0 .0 .0 9 4 0 .0 4 0 .0 1 Jun Jul Au g Sep TRANSPORT EVALUATION EEL RFI SITE SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.107E+11 6.775E+02 0.000E+00 0.000E+00 1.425E+02 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.362E+02 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.764E+12 2.175E+12 2.176E+12 3.641E+08 Percent of Total 18.88 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 81.10 99.98 Maximum leachate concentration: 5.424E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,1-DCE C:\SEV7 WIN7\DICHLOROETHENE, 1,1-.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Starting Depth: 351.00 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 1 2 2 .0 0 E + 1 2 1 .0 0 E + 1 2 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E + 0 2 Concentration (mg/L) 5 .0 0 E + 0 2 4 .0 0 E + 0 2 3 .0 0 E + 0 2 2 .0 0 E + 0 2 1 .0 0 E + 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 4 5 0 2 0 4 0 6 0 - 3 5 0 - 3 5 5 Depth (cm) - 3 6 0 - 3 6 5 - 3 7 0 - 3 7 5 - 3 8 0 - 3 8 5 - 3 9 0 - 3 9 5 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.25E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.61E-2 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 58.90 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 9.00E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 1.04E-5 Neutral Hydrolysis 96.90 Acid Hydrolysis (L/mol/day) 0.00 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,1-DCE C:\SEV7 WIN7\DICHLOROETHENE, 1,1-.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Sublayer Loads 1 Layer 1 (ug/g) 2.61E+01 Layer 2 (ug/g) 2.61E+01 Layer 3 (ug/g) 2.61E+01 Layer 4 (ug/g) 2.61E+01 2 3 4 5 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 10 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 0 .8 0 .6 .0 8 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2.61E+01 0 .9 Load Layer 1 0 .8 ug/cm2 7 2.61E+01 2.61E+01 2.61E+01 2.61E+01 1 .0 1 .0 0 6 2.61E+01 2.61E+01 2.61E+01 2.61E+01 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.037E+10 2.298E+01 0.000E+00 0.000E+00 1.688E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.792E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.214E+11 3.518E+11 3.519E+11 5.654E+07 Percent of Total 8.63 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 91.35 99.98 Maximum leachate concentration: 1.569E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Trans-1,2-Dichloroethylene C:\SEV7 WIN7\TRANS-1,2-DCE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) TRANS-1,2-DCE.APL Starting Depth: 356.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 1 1 3 .0 0 E + 1 1 2 .0 0 E + 1 1 1 .0 0 E + 1 1 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .8 0 E + 0 2 1 .6 0 E + 0 2 Concentration (mg/L) 1 .4 0 E + 0 2 1 .2 0 E + 0 2 1 .0 0 E + 0 2 8 .0 0 E + 0 1 6 .0 0 E + 0 1 4 .0 0 E + 0 1 2 .0 0 E + 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 5 0 0 2 0 4 0 6 0 - 3 5 5 - 3 6 0 Depth (cm) - 3 6 5 - 3 7 0 - 3 7 5 - 3 8 0 - 3 8 5 - 3 9 0 - 3 9 5 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 6.30E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.67E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 52.50 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 7.07E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 1.19E-5 Neutral Hydrolysis 96.90 Acid Hydrolysis (L/mol/day) 0.00 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Trans-1,2-Dichloroethylene C:\SEV7 WIN7\TRANS-1,2-DCE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) TRANS-1,2-DCE.APL Sublayer Loads 1 Layer 1 (ug/g) 4.22E+00 Layer 2 (ug/g) 4.22E+00 Layer 3 (ug/g) 4.22E+00 Layer 4 (ug/g) 4.22E+00 2 3 4 5 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 10 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 0 .8 0 .6 .0 8 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 4.22E+00 0 .9 Load Layer 1 0 .8 ug/cm2 7 4.22E+00 4.22E+00 4.22E+00 4.22E+00 1 .0 1 .0 0 6 4.22E+00 4.22E+00 4.22E+00 4.22E+00 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.756E+02 1.432E-01 0.000E+00 0.000E+00 1.977E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.359E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.977E+09 1.990E+09 1.232E+07 Percent of Total 0.00 0.00 0.00 0.00 99.38 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.38 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Bis(2-ethylhexyl)phthalate C:\SEV7 WIN7\BIS(2-ETHYLHEXYL) PHTHALATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BIS(2-ETHYLHEXYL PHTHALATE).APL Starting Depth: 195.00 cm Ending Depth: 198.90 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 3 .0 0 E + 0 9 2 .0 0 E + 0 9 1 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .340 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.02E-7 Ligand Molecular Weight(g/mol) 0.00 1.5E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.51E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 3.66E-6 Neutral Hydrolysis 391.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Bis(2-ethylhexyl)phthalate C:\SEV7 WIN7\BIS(2-ETHYLHEXYL) PHTHALATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BIS(2-ETHYLHEXYL PHTHALATE).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.87E-02 2.87E-02 2.87E-02 2.96E-02 3.05E-02 3.14E-02 3.23E-02 3.32E-02 3.41E-02 3.50E-02 Layer 2 (ug/g) 3.59E-02 3.68E-02 3.77E-02 3.86E-02 3.95E-02 4.04E-02 4.13E-02 4.22E-02 4.31E-02 4.40E-02 Layer 3 (ug/g) 4.49E-02 4.58E-02 4.67E-02 4.76E-02 4.85E-02 4.94E-02 5.03E-02 5.03E-02 5.03E-02 5.03E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.012E+05 4.028E+01 0.000E+00 0.000E+00 4.681E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.013E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.681E+09 4.691E+09 9.788E+06 Percent of Total 0.00 0.00 0.00 0.00 99.79 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.79 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Di-n-octyl Phthalate C:\SEV7 WIN7\DI-N-OCTYL PHTHALATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) DI-N-OCTYL PHTHALATE.APL Starting Depth: 195.00 cm Ending Depth: 195.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 6 .0 0 E + 0 9 4 .0 0 E + 0 9 2 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.00E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.68E-5 Ligand Molecular Weight(g/mol) 0.00 8.3E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 1.51E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 3.58E-6 Neutral Hydrolysis 391.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Di-n-octyl Phthalate C:\SEV7 WIN7\DI-N-OCTYL PHTHALATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) DI-N-OCTYL PHTHALATE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 Layer 2 (ug/g) 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 Layer 3 (ug/g) 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.134E+05 4.480E+01 0.000E+00 0.000E+00 3.993E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.665E+03 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.438E+08 3.442E+08 3.450E+08 7.561E+05 Percent of Total 0.09 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.68 99.78 Maximum leachate concentration: 1.404E-02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2-Methylnaphthalene \\USWCK1S01\NRII\INDUSTRIAL PROJECTS\ROCKETDYNE\SANTA SUSANA FIELD Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2-METHYLNAPHTHALENE.APL Starting Depth: 197.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 8 3 .0 0 E + 0 8 2 .0 0 E + 0 8 1 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .6 0 E - 0 2 1 .4 0 E - 0 2 Concentration (mg/L) 1 .2 0 E - 0 2 1 .0 0 E - 0 2 8 .0 0 E - 0 3 6 .0 0 E - 0 3 4 .0 0 E - 0 3 2 .0 0 E - 0 3 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 25.4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 4.52E-4 Ligand Molecular Weight(g/mol) 0.00 4320.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 6.29E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.20E-6 Neutral Hydrolysis 142.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2-Methylnaphthalene \\USWCK1S01\NRII\INDUSTRIAL PROJECTS\ROCKETDYNE\SANTA SUSANA FIELD LABORATORY\DQO EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2-METHYLNAPHTHALENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 1.40E-03 2.00E-03 2.50E-03 3.00E-03 Layer 2 (ug/g) 3.50E-03 4.10E-03 4.60E-03 5.10E-03 5.70E-03 6.20E-03 6.70E-03 7.20E-03 7.80E-03 8.30E-03 Layer 3 (ug/g) 8.80E-03 9.40E-03 9.90E-03 1.04E-02 1.09E-02 1.15E-02 1.20E-02 1.20E-02 1.20E-02 1.20E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.172E+06 7.086E+02 0.000E+00 0.000E+00 3.019E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.683E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.208E+08 3.251E+08 3.256E+08 4.758E+05 Percent of Total 0.36 0.00 0.00 0.00 0.93 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 98.54 99.85 Maximum leachate concentration: 8.233E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Acenaphthene C:\SEV7 WIN7\ACENAPHTHENE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ACENAPHTHENE.APL Starting Depth: 196.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 8 3 .0 0 E + 0 8 2 .0 0 E + 0 8 1 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 9 .0 0 E - 0 3 8 .0 0 E - 0 3 Concentration (mg/L) 7 .0 0 E - 0 3 6 .0 0 E - 0 3 5 .0 0 E - 0 3 4 .0 0 E - 0 3 3 .0 0 E - 0 3 2 .0 0 E - 0 3 1 .0 0 E - 0 3 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 4.24 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.55E-4 Ligand Molecular Weight(g/mol) 0.00 7080.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 4.21E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.69E-6 Neutral Hydrolysis 154.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Acenaphthene C:\SEV7 WIN7\ACENAPHTHENE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ACENAPHTHENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.70E-02 1.70E-02 1.70E-02 1.70E-02 1.70E-02 1.70E-02 1.61E-02 1.52E-02 1.43E-02 1.34E-02 Layer 2 (ug/g) 1.25E-02 1.16E-02 1.07E-02 9.80E-03 9.00E-03 8.10E-03 7.20E-03 6.30E-03 5.40E-03 4.50E-03 Layer 3 (ug/g) 3.60E-03 2.70E-03 1.80E-03 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 7.120E+04 In Soil Air 7.042E+00 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.621E+04 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.056E+03 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 7.530E+07 Total Output 7.539E+07 Total Input 7.533E+07 Input - Output -6.649E+04 Percent of Total 0.09 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 100.09 Maximum leachate concentration: 4.677E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Acenaphthylene C:\SEV7 WIN7\ACENAPHTHYLENE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ACENAPHTHYLENE.APL Starting Depth: 199.00 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 7 6 .0 0 E + 0 7 4 .0 0 E + 0 7 2 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 5 .0 0 E - 0 3 4 .5 0 E - 0 3 Concentration (mg/L) 4 .0 0 E - 0 3 3 .5 0 E - 0 3 3 .0 0 E - 0 3 2 .5 0 E - 0 3 2 .0 0 E - 0 3 1 .5 0 E - 0 3 1 .0 0 E - 0 3 5 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 16.1 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.12E-4 Ligand Molecular Weight(g/mol) 0.00 2760.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 4.40E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.52E-6 Neutral Hydrolysis 152.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Acenaphthylene C:\SEV7 WIN7\ACENAPHTHYLENE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ACENAPHTHYLENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 1.00E-03 1.00E-03 1.10E-03 1.10E-03 Layer 2 (ug/g) 1.20E-03 1.20E-03 1.30E-03 1.40E-03 1.40E-03 1.50E-03 1.50E-03 1.60E-03 1.60E-03 1.70E-03 Layer 3 (ug/g) 1.80E-03 1.80E-03 1.90E-03 1.90E-03 2.00E-03 2.00E-03 2.10E-03 2.10E-03 2.10E-03 2.10E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.279E+06 5.165E+04 0.000E+00 0.000E+00 2.234E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.365E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.220E+07 2.291E+09 2.311E+09 1.915E+07 Percent of Total 0.06 0.00 0.00 0.00 96.70 0.00 0.00 0.00 0.00 0.00 0.00 0.59 0.00 0.00 0.00 0.00 1.83 99.17 Maximum leachate concentration: 2.707E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Anthracene C:\SEV7 WIN7\ANTHRACENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ANTHRACENE.APL Starting Depth: 195.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 9 2 .0 0 E + 0 9 1 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .0 0 E - 0 3 Concentration (mg/L) 2 .5 0 E - 0 3 2 .0 0 E - 0 3 1 .5 0 E - 0 3 1 .0 0 E - 0 3 5 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 4.34E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.36E-5 Ligand Molecular Weight(g/mol) 0.00 29500.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.24E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.74E-6 Neutral Hydrolysis 178.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Anthracene C:\SEV7 WIN7\ANTHRACENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ANTHRACENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.30E-01 1.30E-01 1.30E-01 1.30E-01 1.30E-01 1.30E-01 1.23E-01 1.16E-01 1.08E-01 1.01E-01 Layer 2 (ug/g) 9.41E-02 8.70E-02 7.98E-02 7.26E-02 6.55E-02 5.83E-02 5.11E-02 4.39E-02 3.68E-02 2.96E-02 Layer 3 (ug/g) 2.24E-02 1.52E-02 8.10E-03 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 9.934E+05 1.243E+03 0.000E+00 0.000E+00 1.411E+10 0.000E+00 0.000E+00 6.966E+09 0.000E+00 0.000E+00 0.000E+00 6.389E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.108E+10 2.112E+10 3.244E+07 Percent of Total 0.00 0.00 0.00 0.00 66.83 0.00 0.00 32.98 0.00 0.00 0.00 0.03 0.00 0.00 0.00 0.00 0.00 99.85 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Benzo(a)anthracene C:\SEV7 WIN7\BENZO(A)ANTHRACENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(A)ANTHRACENE.APL Starting Depth: 195.00 cm Ending Depth: 266.50 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 3 .0 0 E + 1 0 2 .0 0 E + 1 0 1 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 9.40E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 3.27E-6 Ligand Molecular Weight(g/mol) 0.00 398000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 5.10E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.00E-6 Neutral Hydrolysis 228.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Benzo(a)anthracene C:\SEV7 WIN7\BENZO(A)ANTHRACENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(A)ANTHRACENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.20E+00 1.20E+00 1.20E+00 1.20E+00 1.20E+00 1.20E+00 1.13E+00 1.07E+00 1.00E+00 9.34E-01 Layer 2 (ug/g) 8.67E-01 8.00E-01 7.34E-01 6.67E-01 6.01E-01 5.34E-01 4.67E-01 4.01E-01 3.34E-01 2.68E-01 Layer 3 (ug/g) 2.01E-01 1.34E-01 6.77E-02 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.790E+05 1.318E+02 0.000E+00 0.000E+00 1.161E+10 0.000E+00 0.000E+00 1.362E+09 0.000E+00 0.000E+00 0.000E+00 2.051E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.297E+10 1.302E+10 4.307E+07 Percent of Total 0.00 0.00 0.00 0.00 89.19 0.00 0.00 10.46 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.00 99.67 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Benzo(a)pyrene C:\SEV7 WIN7\BENZO(A)PYRENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(A)PYRENE.APL Starting Depth: 195.00 cm Ending Depth: 224.50 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 1 .5 0 E + 1 0 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.62E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.08E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 1020000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 4.30E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.00E-6 Neutral Hydrolysis 252.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Benzo(a)pyrene C:\SEV7 WIN7\BENZO(A)PYRENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(A)PYRENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 7.40E-01 7.40E-01 7.40E-01 7.40E-01 7.40E-01 7.40E-01 6.99E-01 6.58E-01 6.17E-01 5.76E-01 Layer 2 (ug/g) 5.35E-01 4.94E-01 4.52E-01 4.11E-01 3.70E-01 3.29E-01 2.88E-01 2.47E-01 2.06E-01 1.65E-01 Layer 3 (ug/g) 1.24E-01 8.29E-02 4.18E-02 7.00E-04 7.50E-04 7.50E-04 7.50E-04 7.50E-04 7.50E-04 7.50E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.257E+07 1.251E+04 0.000E+00 0.000E+00 1.353E+10 0.000E+00 0.000E+00 4.000E+09 0.000E+00 0.000E+00 0.000E+00 1.983E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.755E+10 1.760E+10 4.511E+07 Percent of Total 0.07 0.00 0.00 0.00 76.93 0.00 0.00 22.73 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 99.74 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Benzo(b)fluoranthene C:\SEV7 WIN7\BENZO(B)FLUORANTHENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(B)FLUORANTHENE.APL Starting Depth: 195.00 cm Ending Depth: 220.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I 2 .0 0 E + 1 0 1 .5 0 E + 1 0 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.50E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.06E-4 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 1230000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 2.26E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.56E-6 Neutral Hydrolysis 252.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Benzo(b)fluoranthene C:\SEV7 WIN7\BENZO(B)FLUORANTHENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(B)FLUORANTHENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 9.45E-01 8.89E-01 8.34E-01 7.78E-01 Layer 2 (ug/g) 7.23E-01 6.67E-01 6.11E-01 5.56E-01 5.00E-01 4.45E-01 3.89E-01 3.34E-01 2.78E-01 2.23E-01 Layer 3 (ug/g) 1.67E-01 1.12E-01 5.64E-02 9.00E-04 8.70E-04 8.70E-04 8.70E-04 8.70E-04 8.70E-04 8.70E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.878E+04 4.944E+01 0.000E+00 0.000E+00 7.172E+09 0.000E+00 0.000E+00 1.978E+09 0.000E+00 0.000E+00 0.000E+00 1.050E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 9.152E+09 9.163E+09 1.093E+07 Percent of Total 0.00 0.00 0.00 0.00 78.28 0.00 0.00 21.59 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 99.88 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Benzo(k)fluoranthene C:\SEV7 WIN7\BENZO(K)FLUORANTHENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(K)FLUORANTHENE.APL Starting Depth: 195.00 cm Ending Depth: 220.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 8.00E-4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 7.91E-7 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 1230000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 2.26E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.56E-6 Neutral Hydrolysis 252.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Benzo(k)fluoranthene C:\SEV7 WIN7\BENZO(K)FLUORANTHENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BENZO(K)FLUORANTHENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 5.20E-01 5.20E-01 5.20E-01 5.20E-01 5.20E-01 5.20E-01 4.91E-01 4.62E-01 4.33E-01 4.05E-01 Layer 2 (ug/g) 3.76E-01 3.47E-01 3.18E-01 2.89E-01 2.61E-01 2.32E-01 2.03E-01 1.74E-01 1.45E-01 1.16E-01 Layer 3 (ug/g) 8.74E-02 5.86E-02 2.97E-02 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.811E+07 In Soil Air 1.769E+04 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 7.107E+09 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 1.926E+10 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 3.217E+06 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 0.000E+00 Total Output 2.639E+10 Total Input 2.639E+10 Input - Output -3.571E+06 Percent of Total 0.07 0.00 0.00 0.00 26.93 0.00 0.00 73.00 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 100.01 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Chrysene C:\SEV7 WIN7\CHRYSENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) CHRYSENE.APL Starting Depth: 195.00 cm Ending Depth: 266.50 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 3 .0 0 E + 1 0 2 .0 0 E + 1 0 1 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.60E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.24E-5 Ligand Molecular Weight(g/mol) 0.00 398000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.48E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.21E-6 Neutral Hydrolysis 228.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Chrysene C:\SEV7 WIN7\CHRYSENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) CHRYSENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.50E+00 1.50E+00 1.50E+00 1.50E+00 1.50E+00 1.50E+00 1.42E+00 1.33E+00 1.25E+00 1.17E+00 Layer 2 (ug/g) 1.08E+00 1.00E+00 9.17E-01 8.34E-01 7.51E-01 6.67E-01 5.84E-01 5.01E-01 4.17E-01 3.34E-01 Layer 3 (ug/g) 2.51E-01 1.68E-01 8.44E-02 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.414E+02 6.720E-02 0.000E+00 0.000E+00 1.701E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.067E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.701E+09 1.714E+09 1.265E+07 Percent of Total 0.00 0.00 0.00 0.00 99.26 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.26 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Dibenzo(a,h)anthracene C:\SEV7 WIN7\DIBENZO(A,H)ANTHRACENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) DIBENZO(A,H)ANTHRACENE.APL Starting Depth: 195.00 cm Ending Depth: 204.90 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 2 .0 0 E + 0 9 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.49E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.40E-8 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 3800000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 2.02E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.18E-6 Neutral Hydrolysis 278.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Dibenzo(a,h)anthracene C:\SEV7 WIN7\DIBENZO(A,H)ANTHRACENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) DIBENZO(A,H)ANTHRACENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.60E-02 9.60E-02 9.60E-02 9.60E-02 9.60E-02 9.60E-02 9.07E-02 8.54E-02 8.02E-02 7.49E-02 Layer 2 (ug/g) 6.96E-02 6.43E-02 5.90E-02 5.37E-02 4.85E-02 4.32E-02 3.79E-02 3.26E-02 2.73E-02 2.20E-02 Layer 3 (ug/g) 1.68E-02 1.15E-02 6.20E-03 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.380E+04 2.990E+00 0.000E+00 0.000E+00 6.326E+08 0.000E+00 0.000E+00 3.960E+09 0.000E+00 0.000E+00 0.000E+00 3.284E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.593E+09 4.595E+09 1.369E+06 Percent of Total 0.00 0.00 0.00 0.00 13.77 0.00 0.00 86.20 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Indeno(1,2,3-cd)pyrene C:\SEV7 WIN7\INDENO(1,2,3-CD)PYRENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) INDENO(1,2,3-CD)PYRENE.APL Starting Depth: 195.00 cm Ending Depth: 205.60 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 6 .0 0 E + 0 9 4 .0 0 E + 0 9 2 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.20E-5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.53E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 3470000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 1.90E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.66E-6 Neutral Hydrolysis 276.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Indeno(1,2,3-cd)pyrene C:\SEV7 WIN7\INDENO(1,2,3-CD)PYRENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) INDENO(1,2,3-CD)PYRENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.60E-01 2.60E-01 2.60E-01 2.60E-01 2.60E-01 2.60E-01 2.46E-01 2.31E-01 2.17E-01 2.02E-01 Layer 2 (ug/g) 1.88E-01 1.74E-01 1.59E-01 1.45E-01 1.31E-01 1.16E-01 1.02E-01 8.73E-02 7.29E-02 5.85E-02 Layer 3 (ug/g) 4.41E-02 2.97E-02 1.53E-02 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.289E+06 6.156E+04 0.000E+00 0.000E+00 4.016E+10 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.763E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.343E+03 4.023E+10 4.048E+10 2.468E+08 Percent of Total 0.01 0.00 0.00 0.00 99.21 0.00 0.00 0.00 0.00 0.00 0.00 0.17 0.00 0.00 0.00 0.00 0.00 99.39 Maximum leachate concentration: 6.966E-07 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Fluoranthene C:\SEV7 WIN7\FLUORANTHENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) FLUORANTHENE.APL Starting Depth: 195.10 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 1 0 4 .0 0 E + 1 0 2 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 8 .0 0 E - 0 7 7 .0 0 E - 0 7 Concentration (mg/L) 6 .0 0 E - 0 7 5 .0 0 E - 0 7 4 .0 0 E - 0 7 3 .0 0 E - 0 7 2 .0 0 E - 0 7 1 .0 0 E - 0 7 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .206 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.53E-5 Ligand Molecular Weight(g/mol) 0.00 107000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.02E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.35E-6 Neutral Hydrolysis 202.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Fluoranthene C:\SEV7 WIN7\FLUORANTHENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) FLUORANTHENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.30E+00 2.30E+00 2.30E+00 2.30E+00 2.30E+00 2.30E+00 2.17E+00 2.04E+00 1.92E+00 1.79E+00 Layer 2 (ug/g) 1.66E+00 1.53E+00 1.41E+00 1.28E+00 1.15E+00 1.02E+00 8.96E-01 7.68E-01 6.41E-01 5.13E-01 Layer 3 (ug/g) 3.85E-01 2.57E-01 1.30E-01 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 2.560E+05 6.524E+03 0.000E+00 0.000E+00 1.320E+08 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.724E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.553E+08 2.894E+08 2.904E+08 9.738E+05 Percent of Total 0.09 0.00 0.00 0.00 45.47 0.00 0.00 0.00 0.00 0.00 0.00 0.59 0.00 0.00 0.00 0.00 53.51 99.66 Maximum leachate concentration: 3.828E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Fluorene C:\SEV7 WIN7\FLUORENE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) FLUORENE.APL Starting Depth: 195.80 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 8 3 .0 0 E + 0 8 2 .0 0 E + 0 8 1 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 3 4 .0 0 E - 0 3 Concentration (mg/L) 3 .5 0 E - 0 3 3 .0 0 E - 0 3 2 .5 0 E - 0 3 2 .0 0 E - 0 3 1 .5 0 E - 0 3 1 .0 0 E - 0 3 5 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.98 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.36E-5 Ligand Molecular Weight(g/mol) 0.00 13800.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.63E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.88E-6 Neutral Hydrolysis 166.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Fluorene C:\SEV7 WIN7\FLUORENE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) FLUORENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.50E-02 1.50E-02 1.50E-02 1.50E-02 1.50E-02 1.50E-02 1.42E-02 1.34E-02 1.27E-02 1.19E-02 Layer 2 (ug/g) 1.11E-02 1.03E-02 9.50E-03 8.70E-03 8.00E-03 7.20E-03 6.40E-03 5.60E-03 4.80E-03 4.00E-03 Layer 3 (ug/g) 3.20E-03 2.50E-03 1.70E-03 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.001E+06 In Soil Air 1.712E+01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 6.611E+03 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.957E+02 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 6.786E+07 Total Output 6.887E+07 Total Input 6.882E+07 Input - Output -5.317E+04 Percent of Total 1.46 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 98.61 100.08 Maximum leachate concentration: 5.648E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Naphthalene C:\SEV7 WIN7\NAPHTHALENE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) NAPHTHALENE.APL Starting Depth: 200.20 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 7 6 .0 0 E + 0 7 4 .0 0 E + 0 7 2 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E - 0 3 Concentration (mg/L) 5 .0 0 E - 0 3 4 .0 0 E - 0 3 3 .0 0 E - 0 3 2 .0 0 E - 0 3 1 .0 0 E - 0 3 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 31.0 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 4.83E-4 Ligand Molecular Weight(g/mol) 0.00 2000.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 5.90E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.50E-6 Neutral Hydrolysis 128.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Naphthalene C:\SEV7 WIN7\NAPHTHALENE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) NAPHTHALENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.10E-03 2.10E-03 2.00E-03 2.00E-03 Layer 2 (ug/g) 1.90E-03 1.80E-03 1.80E-03 1.70E-03 1.60E-03 1.60E-03 1.50E-03 1.50E-03 1.40E-03 1.30E-03 Layer 3 (ug/g) 1.30E-03 1.20E-03 1.10E-03 1.10E-03 1.00E-03 1.00E-03 9.00E-04 9.00E-04 9.00E-04 9.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 5.974E+06 2.430E+05 0.000E+00 0.000E+00 1.445E+10 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.137E+08 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.306E+09 1.588E+10 1.603E+10 1.437E+08 Percent of Total 0.04 0.00 0.00 0.00 90.20 0.00 0.00 0.00 0.00 0.00 0.00 0.71 0.00 0.00 0.00 0.00 8.15 99.10 Maximum leachate concentration: 6.683E-02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Phenanthrene C:\SEV7 WIN7\PHENANTHRENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) PHENANTHRENE.APL Starting Depth: 195.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 1 0 1 .5 0 E + 1 0 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 8 .0 0 E - 0 2 7 .0 0 E - 0 2 Concentration (mg/L) 6 .0 0 E - 0 2 5 .0 0 E - 0 2 4 .0 0 E - 0 2 3 .0 0 E - 0 2 2 .0 0 E - 0 2 1 .0 0 E - 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.15 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 3.59E-5 Ligand Molecular Weight(g/mol) 0.00 22900.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.33E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.48E-6 Neutral Hydrolysis 178.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Phenanthrene C:\SEV7 WIN7\PHENANTHRENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) PHENANTHRENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.10E-01 9.10E-01 9.10E-01 9.10E-01 9.10E-01 9.10E-01 8.59E-01 8.09E-01 7.59E-01 7.08E-01 Layer 2 (ug/g) 6.58E-01 6.07E-01 5.57E-01 5.06E-01 4.56E-01 4.05E-01 3.55E-01 3.04E-01 2.54E-01 2.03E-01 Layer 3 (ug/g) 1.53E-01 1.02E-01 5.20E-02 1.50E-03 1.50E-03 1.50E-03 1.50E-03 1.50E-03 1.50E-03 1.50E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.009E+06 4.332E+04 0.000E+00 0.000E+00 3.857E+10 0.000E+00 0.000E+00 5.230E+09 0.000E+00 0.000E+00 0.000E+00 6.620E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.418E+03 4.387E+10 4.399E+10 1.128E+08 Percent of Total 0.01 0.00 0.00 0.00 87.70 0.00 0.00 11.89 0.00 0.00 0.00 0.15 0.00 0.00 0.00 0.00 0.00 99.74 Maximum leachate concentration: 6.872E-07 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Pyrene C:\SEV7 WIN7\PYRENE (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) PYRENE.APL Starting Depth: 195.10 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 1 0 4 .0 0 E + 1 0 2 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 8 .0 0 E - 0 7 7 .0 0 E - 0 7 Concentration (mg/L) 6 .0 0 E - 0 7 5 .0 0 E - 0 7 4 .0 0 E - 0 7 3 .0 0 E - 0 7 2 .0 0 E - 0 7 1 .0 0 E - 0 7 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .135 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.10E-5 Ligand Molecular Weight(g/mol) 0.00 105000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.72E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.24E-6 Neutral Hydrolysis 202.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Pyrene C:\SEV7 WIN7\PYRENE (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) PYRENE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.50E+00 2.50E+00 2.50E+00 2.50E+00 2.50E+00 2.50E+00 2.36E+00 2.22E+00 2.08E+00 1.94E+00 Layer 2 (ug/g) 1.81E+00 1.67E+00 1.53E+00 1.39E+00 1.25E+00 1.11E+00 9.74E-01 8.35E-01 6.96E-01 5.57E-01 Layer 3 (ug/g) 4.19E-01 2.80E-01 1.41E-01 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 2.20E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 0.000E+00 In Soil Air 4.743E-03 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.136E+00 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.694E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 1.219E+09 Total Output 1.219E+09 Total Input 1.219E+09 Input - Output -2.500E+05 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.02 100.02 Maximum leachate concentration: 8.449E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Starting Depth: 220.30 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 9 .0 0 E - 0 1 8 .0 0 E - 0 1 Concentration (mg/L) 7 .0 0 E - 0 1 6 .0 0 E - 0 1 5 .0 0 E - 0 1 4 .0 0 E - 0 1 3 .0 0 E - 0 1 2 .0 0 E - 0 1 1 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.49E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.40E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 6.76 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 117.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.40E-03 2.40E-03 2.40E-03 2.40E-03 2.40E-03 2.40E-03 4.30E-03 6.20E-03 8.20E-03 1.01E-02 Layer 2 (ug/g) 1.20E-02 1.40E-02 1.59E-02 1.78E-02 1.98E-02 2.17E-02 2.36E-02 2.56E-02 2.75E-02 2.95E-02 Layer 3 (ug/g) 3.14E-02 3.33E-02 3.53E-02 3.72E-02 3.91E-02 4.11E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.812E+06 1.860E+04 0.000E+00 0.000E+00 4.661E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.105E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.669E+09 4.691E+09 2.181E+07 Percent of Total 0.15 0.00 0.00 0.00 99.37 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.00 99.53 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Aroclor 1254 (Median) C:\SEV7 WIN7\AROCLOR 1254.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) AROCLOR 1254.APL Starting Depth: 195.00 cm Ending Depth: 233.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 6 .0 0 E + 0 9 4 .0 0 E + 0 9 2 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.00E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.83E-4 Ligand Molecular Weight(g/mol) 0.00 760000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 4.79E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.99E-6 Neutral Hydrolysis 331.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Aroclor 1254 (Median) C:\SEV7 WIN7\AROCLOR 1254.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) AROCLOR 1254.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 Layer 2 (ug/g) 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 Layer 3 (ug/g) 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 9.90E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.613E+07 4.558E+03 0.000E+00 0.000E+00 1.097E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.683E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.113E+09 1.121E+09 7.018E+06 Percent of Total 1.44 0.00 0.00 0.00 97.93 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.37 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Aroclor 1260 (Median) C:\SEV7 WIN7\AROCLOR 1260.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) AROCLOR 1260.APL Starting Depth: 195.00 cm Ending Depth: 202.80 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.27E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.08E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 5370000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 3.53E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.12E-6 Neutral Hydrolysis 377.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Aroclor 1260 (Median) C:\SEV7 WIN7\AROCLOR 1260.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) AROCLOR 1260.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.60E-02 4.60E-02 4.46E-02 4.32E-02 4.17E-02 4.03E-02 3.89E-02 3.75E-02 3.61E-02 3.46E-02 Layer 2 (ug/g) 3.32E-02 3.18E-02 3.04E-02 2.90E-02 2.75E-02 2.61E-02 2.47E-02 2.33E-02 2.19E-02 2.04E-02 Layer 3 (ug/g) 1.90E-02 1.76E-02 1.62E-02 1.48E-02 1.33E-02 1.19E-02 1.05E-02 1.05E-02 1.05E-02 1.05E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 8.221E+01 7.671E-06 0.000E+00 0.000E+00 4.938E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.810E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.454E+08 8.454E+08 8.456E+08 1.158E+05 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 99.99 Maximum leachate concentration: 3.783E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Starting Depth: 209.80 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .0 0 E - 0 1 3 .5 0 E - 0 1 Concentration (mg/L) 3 .0 0 E - 0 1 2 .5 0 E - 0 1 2 .0 0 E - 0 1 1 .5 0 E - 0 1 1 .0 0 E - 0 1 5 .0 0 E - 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 55.3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.68E-09 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 185.00 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 4.60E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 1.17E-6 Neutral Hydrolysis 221.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 3.20E-02 3.20E-02 3.11E-02 3.02E-02 2.93E-02 2.84E-02 2.75E-02 2.66E-02 2.57E-02 2.48E-02 Layer 2 (ug/g) 2.39E-02 2.30E-02 2.21E-02 2.12E-02 2.03E-02 1.94E-02 1.85E-02 1.76E-02 1.67E-02 1.58E-02 Layer 3 (ug/g) 1.49E-02 1.40E-02 1.31E-02 1.22E-02 1.13E-02 1.04E-02 9.50E-03 9.50E-03 9.50E-03 9.50E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 2.374E+03 7.149E-06 0.000E+00 0.000E+00 1.639E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.301E+10 6.301E+10 6.302E+10 7.850E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 99.99 Maximum leachate concentration: 4.328E+01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Starting Depth: 216.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 1 0 6 .0 0 E + 1 0 4 .0 0 E + 1 0 2 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 5 .0 0 E + 0 1 4 .5 0 E + 0 1 Concentration (mg/L) 4 .0 0 E + 0 1 3 .5 0 E + 0 1 3 .0 0 E + 0 1 2 .5 0 E + 0 1 2 .0 0 E + 0 1 1 .5 0 E + 0 1 1 .0 0 E + 0 1 5 .0 0 E + 0 0 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 825.0 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.11E-09 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 51.80 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 5.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.42E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.40E-01 9.40E-01 9.66E-01 9.93E-01 1.02E+00 1.05E+00 1.07E+00 1.10E+00 1.25E-01 1.15E+00 Layer 2 (ug/g) 1.18E+00 1.20E+00 1.23E+00 1.26E+00 1.28E+00 1.31E+00 1.34E+00 1.36E+00 1.39E+00 1.42E+00 Layer 3 (ug/g) 1.44E+00 1.47E+00 1.49E+00 1.52E+00 1.55E+00 1.57E+00 1.60E+00 1.60E+00 1.60E+00 1.60E+00 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 2.661E+00 In Soil Air 5.180E-04 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.385E+04 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 9.597E+02 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 5.690E+07 Total Output 5.692E+07 Total Input 5.686E+07 Input - Output -6.009E+04 Percent of Total 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.08 100.11 Maximum leachate concentration: 3.741E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Silvex C:\SEV7 WIN7\SILVEX 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SILVEX.APL Starting Depth: 199.20 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 0 7 4 .0 0 E + 0 7 2 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .0 0 E - 0 3 3 .5 0 E - 0 3 Concentration (mg/L) 3 .0 0 E - 0 3 2 .5 0 E - 0 3 2 .0 0 E - 0 3 1 .5 0 E - 0 3 1 .0 0 E - 0 3 5 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 106.0 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.07E-9 Ligand Molecular Weight(g/mol) 0.00 2600.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 1.94E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.85E-6 Neutral Hydrolysis 270.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Silvex C:\SEV7 WIN7\SILVEX 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SILVEX.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 9.00E-04 1.00E-03 1.00E-03 1.00E-03 1.00E-03 Layer 2 (ug/g) 1.00E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.20E-03 1.20E-03 1.20E-03 1.20E-03 1.20E-03 Layer 3 (ug/g) 1.30E-03 1.30E-03 1.30E-03 1.30E-03 1.40E-03 1.40E-03 1.40E-03 1.40E-03 1.40E-03 1.40E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.588E+02 4.746E+01 0.000E+00 0.000E+00 6.842E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.208E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.821E-01 6.854E+07 6.870E+07 1.546E+05 Percent of Total 0.00 0.00 0.00 0.00 99.60 0.00 0.00 0.00 0.00 0.00 0.00 0.18 0.00 0.00 0.00 0.00 0.00 99.77 Maximum leachate concentration: 1.001E-11 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 4,4'-DDD (Dichlorodiphenyldichloroethane) C:\SEV7 WIN7\4,4'-DDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 4,4'-DDD.APL Starting Depth: 195.10 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 7 6 .0 0 E + 0 7 4 .0 0 E + 0 7 2 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E - 1 1 Concentration (mg/L) 1 .0 0 E - 1 1 8 .0 0 E - 1 2 6 .0 0 E - 1 2 4 .0 0 E - 1 2 2 .0 0 E - 1 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 6.76E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.60E-6 Ligand Molecular Weight(g/mol) 0.00 102000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.88E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.76E-6 Neutral Hydrolysis 320.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 4,4'-DDD (Dichlorodiphenyldichloroethane) C:\SEV7 WIN7\4,4'-DDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 4,4'-DDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 8.50E-04 8.50E-04 9.00E-04 9.00E-04 1.00E-03 1.00E-03 1.00E-03 1.10E-03 1.10E-03 1.20E-03 Layer 2 (ug/g) 1.20E-03 1.20E-03 1.30E-03 1.30E-03 1.30E-03 1.40E-03 1.40E-03 1.50E-03 1.50E-03 1.60E-03 Layer 3 (ug/g) 1.60E-03 1.60E-03 1.60E-03 1.70E-03 1.70E-03 1.80E-03 1.80E-03 1.80E-03 1.80E-03 1.80E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.167E+04 3.347E+02 0.000E+00 0.000E+00 8.943E+08 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.127E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.949E+08 9.002E+08 5.229E+06 Percent of Total 0.00 0.00 0.00 0.00 99.35 0.00 0.00 0.00 0.00 0.00 0.00 0.07 0.00 0.00 0.00 0.00 0.00 99.42 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 4,4'-DDT (Dichlorodiphenyltrichloroethane) C:\SEV7 WIN7\4,4'-DDT.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 4,4'-DDT.APL Starting Depth: 195.00 cm Ending Depth: 301.60 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 6.51E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.18E-6 Ligand Molecular Weight(g/mol) 0.00 263000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.92E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.43E-6 Neutral Hydrolysis 354.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 4,4'-DDT (Dichlorodiphenyltrichloroethane) C:\SEV7 WIN7\4,4'-DDT.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 4,4'-DDT.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 Layer 2 (ug/g) 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 Layer 3 (ug/g) 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 1.90E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.676E+02 In Soil Air 4.768E-02 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.986E+04 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.161E+03 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 2.500E+07 Total Output 2.502E+07 Total Input 2.496E+07 Input - Output -6.639E+04 Percent of Total 0.00 0.00 0.00 0.00 0.08 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.18 100.27 Maximum leachate concentration: 1.400E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Starting Depth: 198.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .6 0 E - 0 3 1 .4 0 E - 0 3 Concentration (mg/L) 1 .2 0 E - 0 3 1 .0 0 E - 0 3 8 .0 0 E - 0 4 6 .0 0 E - 0 4 4 .0 0 E - 0 4 2 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 4.52 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.90E-7 Ligand Molecular Weight(g/mol) 0.00 3080.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.10E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.37E-6 Neutral Hydrolysis 291.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 7.30E-04 7.30E-04 7.20E-04 7.00E-04 6.90E-04 6.80E-04 6.70E-04 6.50E-04 6.40E-04 6.30E-04 Layer 2 (ug/g) 6.10E-04 6.00E-04 5.90E-04 5.70E-04 5.60E-04 5.50E-04 5.40E-04 5.20E-04 5.10E-04 5.00E-04 Layer 3 (ug/g) 4.80E-04 4.70E-04 4.60E-04 4.40E-04 4.30E-04 4.20E-04 4.10E-04 4.10E-04 4.10E-04 4.10E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.815E+04 In Soil Air 6.092E-01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.947E+03 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 2.192E+02 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 2.361E+07 Total Output 2.363E+07 Total Input 2.361E+07 Input - Output -2.147E+04 Percent of Total 0.08 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.09 Maximum leachate concentration: 2.400E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Endosulfan I C:\SEV7 WIN7\ENDOSULFAN I.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ENDOSULFAN I.APL Starting Depth: 200.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .0 0 E - 0 3 Concentration (mg/L) 2 .5 0 E - 0 3 2 .0 0 E - 0 3 1 .5 0 E - 0 3 1 .0 0 E - 0 3 5 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .530 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 4.67E-5 Ligand Molecular Weight(g/mol) 0.00 1600.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.77E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.27E-6 Neutral Hydrolysis 407.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Endosulfan I C:\SEV7 WIN7\ENDOSULFAN I.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ENDOSULFAN I.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 5.50E-04 5.50E-04 5.50E-04 5.40E-04 5.40E-04 5.40E-04 5.30E-04 5.30E-04 5.30E-04 5.20E-04 Layer 2 (ug/g) 5.20E-04 5.20E-04 5.10E-04 5.10E-04 5.10E-04 5.00E-04 5.00E-04 5.00E-04 4.90E-04 4.90E-04 Layer 3 (ug/g) 4.90E-04 4.80E-04 4.80E-04 4.80E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 2.383E+02 In Soil Air 6.631E-02 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.385E+04 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.249E+03 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 3.132E+07 Total Output 3.135E+07 Total Input 3.129E+07 Input - Output -6.098E+04 Percent of Total 0.00 0.00 0.00 0.00 0.08 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.11 100.19 Maximum leachate concentration: 1.583E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Endosulfan Sulfate C:\SEV7 WIN7\ENDOSULFAN SULFATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ENDOSULFAN SULFATE.APL Starting Depth: 198.30 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 7 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .8 0 E - 0 3 1 .6 0 E - 0 3 Concentration (mg/L) 1 .4 0 E - 0 3 1 .2 0 E - 0 3 1 .0 0 E - 0 3 8 .0 0 E - 0 4 6 .0 0 E - 0 4 4 .0 0 E - 0 4 2 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .220 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 8.92E-7 Ligand Molecular Weight(g/mol) 0.00 3440.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.18E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.32E-6 Neutral Hydrolysis 423.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Endosulfan Sulfate C:\SEV7 WIN7\ENDOSULFAN SULFATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ENDOSULFAN SULFATE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 5.50E-04 5.50E-04 5.60E-04 5.60E-04 5.70E-04 5.80E-04 5.90E-04 5.90E-04 6.00E-04 6.10E-04 Layer 2 (ug/g) 6.10E-04 6.20E-04 6.30E-04 6.30E-04 6.40E-04 6.50E-04 6.50E-04 6.60E-04 6.70E-04 6.80E-04 Layer 3 (ug/g) 6.80E-04 6.90E-04 7.00E-04 7.00E-04 7.10E-04 7.20E-04 7.20E-04 7.30E-04 7.30E-04 7.30E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 4.805E+02 In Soil Air 6.047E+01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 7.060E+06 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.117E+05 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 2.335E+07 Total Output 3.052E+07 Total Input 3.048E+07 Input - Output -4.405E+04 Percent of Total 0.00 0.00 0.00 0.00 23.16 0.00 0.00 0.00 0.00 0.00 0.00 0.37 0.00 0.00 0.00 0.00 76.61 100.14 Maximum leachate concentration: 4.866E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Endrin (Median) C:\SEV7 WIN7\ENDRIN (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ENDRIN.APL Starting Depth: 196.00 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 7 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E - 0 4 Concentration (mg/L) 5 .0 0 E - 0 4 4 .0 0 E - 0 4 3 .0 0 E - 0 4 2 .0 0 E - 0 4 1 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .250 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.10E-6 Ligand Molecular Weight(g/mol) 0.00 11400.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 1.25E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.74E-6 Neutral Hydrolysis 381.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Endrin (Median) C:\SEV7 WIN7\ENDRIN (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ENDRIN.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 5.00E-04 5.00E-04 5.10E-04 5.20E-04 5.30E-04 5.40E-04 5.50E-04 5.50E-04 5.60E-04 5.70E-04 Layer 2 (ug/g) 5.80E-04 5.90E-04 6.00E-04 6.10E-04 6.20E-04 6.30E-04 6.40E-04 6.40E-04 6.50E-04 6.60E-04 Layer 3 (ug/g) 6.70E-04 6.80E-04 6.90E-04 7.00E-04 7.10E-04 7.20E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 8.029E+02 In Soil Air 5.416E+00 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.914E+06 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 4.063E+04 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 4.154E+07 Total Output 4.350E+07 Total Input 4.348E+07 Input - Output -2.464E+04 Percent of Total 0.00 0.00 0.00 0.00 4.40 0.00 0.00 0.00 0.00 0.00 0.00 0.09 0.00 0.00 0.00 0.00 95.56 100.06 Maximum leachate concentration: 9.248E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Endrin Aldehyde C:\SEV7 WIN7\ENDRIN ALDEHYDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ENDRIN ALDEHYDEAPL.APL Starting Depth: 196.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 0 7 4 .0 0 E + 0 7 2 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .0 0 E - 0 3 9 .0 0 E - 0 4 Concentration (mg/L) 8 .0 0 E - 0 4 7 .0 0 E - 0 4 6 .0 0 E - 0 4 5 .0 0 E - 0 4 4 .0 0 E - 0 4 3 .0 0 E - 0 4 2 .0 0 E - 0 4 1 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 4.98E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.24E-6 Ligand Molecular Weight(g/mol) 0.00 8490.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.29E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.12E-6 Neutral Hydrolysis 381.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Endrin Aldehyde C:\SEV7 WIN7\ENDRIN ALDEHYDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ENDRIN ALDEHYDEAPL.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.10E-03 1.00E-03 1.00E-03 1.00E-03 1.00E-03 Layer 2 (ug/g) 1.00E-03 9.80E-04 9.70E-04 9.60E-04 9.50E-04 9.40E-04 9.30E-04 9.10E-04 9.00E-04 8.90E-04 Layer 3 (ug/g) 8.80E-04 8.70E-04 8.60E-04 8.40E-04 8.30E-04 8.20E-04 8.10E-04 8.10E-04 8.10E-04 8.10E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 2.490E+04 In Soil Air 6.463E+03 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.272E+07 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.780E+05 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 2.173E+06 Total Output 2.511E+07 Total Input 2.495E+07 Input - Output -1.611E+05 Percent of Total 0.10 0.03 0.00 0.00 91.10 0.00 0.00 0.00 0.00 0.00 0.00 0.71 0.00 0.00 0.00 0.00 8.71 100.65 Maximum leachate concentration: 1.082E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Starting Depth: 195.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E - 0 4 Concentration (mg/L) 1 .0 0 E - 0 4 8 .0 0 E - 0 5 6 .0 0 E - 0 5 4 .0 0 E - 0 5 2 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .180 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.10E-4 Ligand Molecular Weight(g/mol) 0.00 23000.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 1.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.15E-6 Neutral Hydrolysis 373.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.40E-04 4.40E-04 4.40E-04 4.50E-04 4.50E-04 4.60E-04 4.60E-04 4.70E-04 4.80E-04 4.80E-04 Layer 2 (ug/g) 4.90E-04 4.90E-04 5.00E-04 5.00E-04 5.10E-04 5.20E-04 5.20E-04 5.30E-04 5.30E-04 5.40E-04 Layer 3 (ug/g) 5.50E-04 5.50E-04 5.60E-04 5.60E-04 5.70E-04 5.70E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 6.868E+02 In Soil Air 8.745E+01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.347E+07 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.547E+05 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 8.726E+06 Total Output 2.236E+07 Total Input 2.227E+07 Input - Output -9.029E+04 Percent of Total 0.00 0.00 0.00 0.00 60.52 0.00 0.00 0.00 0.00 0.00 0.00 0.69 0.00 0.00 0.00 0.00 39.18 100.41 Maximum leachate concentration: 2.594E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Starting Depth: 195.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .0 0 E - 0 4 Concentration (mg/L) 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index .200 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.50E-6 Ligand Molecular Weight(g/mol) 0.00 15700.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.19E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 389.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 2 (ug/g) 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 3 (ug/g) 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.086E+06 2.131E+02 0.000E+00 0.000E+00 2.210E+08 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.580E+02 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.221E+08 2.227E+08 5.508E+05 Percent of Total 0.49 0.00 0.00 0.00 99.26 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.75 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Mirex C:\SEV7 WIN7\MIREX 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MIREX.APL Starting Depth: 195.00 cm Ending Depth: 195.80 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 3 .0 0 E + 0 8 2 .0 0 E + 0 8 1 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 4.27E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.42E-3 Ligand Molecular Weight(g/mol) 0.00 7.1E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.41E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 3.08E-6 Neutral Hydrolysis 546.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Mirex C:\SEV7 WIN7\MIREX 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MIREX.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 Layer 2 (ug/g) 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 Layer 3 (ug/g) 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 4.70E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 5.292E+01 6.727E-02 0.000E+00 0.000E+00 2.977E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.501E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.977E+07 3.006E+07 2.872E+05 Percent of Total 0.00 0.00 0.00 0.00 99.04 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.04 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,4,6,7,8-HpCDD (Median) C:\SEV7 WIN7\1,2,3,4,6,7,8-HPCDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,6,7,8-HPCDD.APL Starting Depth: 195.00 cm Ending Depth: 195.90 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 4 .0 0 E + 0 7 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.40E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.33E-5 Ligand Molecular Weight(g/mol) 0.00 6.3E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 2.05E-3 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 425.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,4,6,7,8-HpCDD (Median) C:\SEV7 WIN7\1,2,3,4,6,7,8-HPCDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,6,7,8-HPCDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.50E-03 1.50E-03 1.40E-03 1.40E-03 1.30E-03 1.30E-03 1.20E-03 1.20E-03 1.10E-03 1.10E-03 Layer 2 (ug/g) 1.00E-03 9.40E-04 8.90E-04 8.40E-04 7.80E-04 7.30E-04 6.70E-04 6.20E-04 5.60E-04 5.10E-04 Layer 3 (ug/g) 4.50E-04 4.00E-04 3.40E-04 2.90E-04 2.40E-04 1.80E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.744E+01 1.167E-02 0.000E+00 0.000E+00 8.514E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.942E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.514E+06 8.528E+06 1.373E+04 Percent of Total 0.00 0.00 0.00 0.00 99.84 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.84 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,4,6,7,8-HpCDF C:\SEV7 WIN7\1,2,3,4,6,7,8-HPCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,6,7,8-HPCDF.APL Starting Depth: 195.00 cm Ending Depth: 195.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .0 0 E + 0 7 5 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.35E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.01E-5 Ligand Molecular Weight(g/mol) 0.00 7.9E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 2.40E-2 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 409.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,4,6,7,8-HpCDF C:\SEV7 WIN7\1,2,3,4,6,7,8-HPCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,6,7,8-HPCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 Layer 2 (ug/g) 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 Layer 3 (ug/g) 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 1.80E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.658E+01 3.195E-03 0.000E+00 0.000E+00 7.580E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.441E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.580E+05 7.581E+05 7.796E+01 Percent of Total 0.00 0.00 0.00 0.00 99.99 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,4,7,8,9-HpCDF C:\SEV7 WIN7\1,2,3,4,7,8,9-HPCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,7,8,9-HPCDF.APL Starting Depth: 195.00 cm Ending Depth: 197.40 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 8 .0 0 E + 0 5 6 .0 0 E + 0 5 4 .0 0 E + 0 5 2 .0 0 E + 0 5 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.37E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.87E-6 Ligand Molecular Weight(g/mol) 0.00 2.5E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 2.81E-2 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 409.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,4,7,8,9-HpCDF C:\SEV7 WIN7\1,2,3,4,7,8,9-HPCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,7,8,9-HPCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 Layer 2 (ug/g) 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 Layer 3 (ug/g) 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 1.60E-05 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.010E+01 1.856E-03 0.000E+00 0.000E+00 3.545E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.476E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.545E+05 3.546E+05 6.642E+01 Percent of Total 0.00 0.00 0.00 0.00 99.98 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.98 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,4,7,8-HxCDD C:\SEV7 WIN7\1,2,3,4,7,8-HXCDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,7,8-HXCDD.APL Starting Depth: 195.00 cm Ending Depth: 197.40 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 4 .0 0 E + 0 5 3 .0 0 E + 0 5 2 .0 0 E + 0 5 1 .0 0 E + 0 5 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 6.60E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.26E-5 Ligand Molecular Weight(g/mol) 0.00 2.5E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 1.16E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.12E-6 Neutral Hydrolysis 391.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,4,7,8-HxCDD C:\SEV7 WIN7\1,2,3,4,7,8-HXCDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,7,8-HXCDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.90E-05 1.90E-05 1.80E-05 1.80E-05 1.70E-05 1.60E-05 1.50E-05 1.50E-05 1.40E-05 1.30E-05 Layer 2 (ug/g) 1.20E-05 1.20E-05 1.10E-05 1.00E-05 9.50E-06 8.80E-06 8.00E-06 7.30E-06 6.60E-06 5.80E-06 Layer 3 (ug/g) 5.10E-06 4.40E-06 3.60E-06 2.90E-06 2.10E-06 1.40E-06 6.70E-07 6.70E-07 6.70E-07 6.70E-07 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.268E+01 7.570E-04 0.000E+00 0.000E+00 1.239E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.897E-01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.239E+05 1.240E+05 5.042E+01 Percent of Total 0.01 0.00 0.00 0.00 99.95 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.96 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,4,7,8-HxCDF C:\SEV7 WIN7\1,2,3,4,7,8-HXCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,7,8-HXCDF.APL Starting Depth: 195.00 cm Ending Depth: 197.40 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .5 0 E + 0 5 1 .0 0 E + 0 5 5 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.10E-5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.43E-5 Ligand Molecular Weight(g/mol) 0.00 2.5E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.39E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 375.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,4,7,8-HxCDF C:\SEV7 WIN7\1,2,3,4,7,8-HXCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,4,7,8-HXCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 7.00E-06 7.00E-06 6.70E-06 6.50E-06 6.20E-06 5.90E-06 5.60E-06 5.30E-06 5.10E-06 4.80E-06 Layer 2 (ug/g) 4.50E-06 4.20E-06 3.90E-06 3.70E-06 3.40E-06 3.10E-06 2.80E-06 2.50E-06 2.30E-06 2.00E-06 Layer 3 (ug/g) 1.70E-06 1.40E-06 1.10E-06 8.70E-07 5.90E-07 3.10E-07 2.80E-08 2.80E-08 2.80E-08 2.80E-08 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 8.449E+01 2.379E-02 0.000E+00 0.000E+00 2.850E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.185E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.850E+06 2.871E+06 2.000E+04 Percent of Total 0.00 0.00 0.00 0.00 99.30 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.30 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,6,7,8-HxCDD C:\SEV7 WIN7\1,2,3,6,7,8-HXCDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,6,7,8-HXCDD.APL Starting Depth: 195.00 cm Ending Depth: 197.60 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 4 .0 0 E + 0 6 3 .0 0 E + 0 6 2 .0 0 E + 0 6 1 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 6.00E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.83E-5 Ligand Molecular Weight(g/mol) 0.00 2.3E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.70E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.12E-6 Neutral Hydrolysis 391.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,6,7,8-HxCDD C:\SEV7 WIN7\1,2,3,6,7,8-HXCDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,6,7,8-HXCDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-06 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 Layer 2 (ug/g) 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 Layer 3 (ug/g) 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 6.20E-05 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.772E+01 In Soil Air 1.240E-03 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 1.367E+05 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 1.894E+00 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 0.000E+00 Total Output 1.367E+05 Total Input 1.367E+05 Input - Output -2.150E+01 Percent of Total 0.01 0.00 0.00 0.00 100.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.02 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,6,7,8-HxCDF C:\SEV7 WIN7\1,2,3,6,7,8-HXCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,6,7,8-HXCDF.APL Starting Depth: 195.00 cm Ending Depth: 199.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .5 0 E + 0 5 1 .0 0 E + 0 5 5 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.13E-4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.10E-5 Ligand Molecular Weight(g/mol) 0.00 1.3E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.90E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 375.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,6,7,8-HxCDF C:\SEV7 WIN7\1,2,3,6,7,8-HXCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,6,7,8-HXCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 7.70E-06 7.70E-06 7.40E-06 7.10E-06 6.80E-06 6.50E-06 6.20E-06 5.90E-06 5.60E-06 5.30E-06 Layer 2 (ug/g) 5.00E-06 4.60E-06 4.30E-06 4.00E-06 3.70E-06 3.40E-06 3.10E-06 2.80E-06 2.50E-06 2.20E-06 Layer 3 (ug/g) 1.90E-06 1.60E-06 1.30E-06 9.50E-07 6.40E-07 3.30E-07 2.40E-08 2.40E-08 2.40E-08 2.40E-08 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.036E+01 6.654E-03 0.000E+00 0.000E+00 7.970E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.111E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.971E+05 8.220E+05 2.486E+04 Percent of Total 0.01 0.00 0.00 0.00 96.97 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 96.97 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,7,8,9-HxCDD C:\SEV7 WIN7\1,2,3,7,8,9-HXCDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8,9-HXCDD.APL Starting Depth: 195.00 cm Ending Depth: 197.60 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .0 0 E + 0 6 5 .0 0 E + 0 5 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 6.00E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.83E-5 Ligand Molecular Weight(g/mol) 0.00 2.3E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 2.79E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.12E-6 Neutral Hydrolysis 391.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,7,8,9-HxCDD C:\SEV7 WIN7\1,2,3,7,8,9-HXCDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8,9-HXCDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.20E-05 4.20E-05 4.00E-05 3.90E-05 3.70E-05 3.50E-05 3.40E-05 3.20E-05 3.10E-05 2.90E-05 Layer 2 (ug/g) 2.80E-05 2.60E-05 2.50E-05 2.30E-05 2.20E-05 2.00E-05 1.80E-05 1.70E-05 1.50E-05 1.40E-05 Layer 3 (ug/g) 1.20E-05 1.10E-05 9.20E-06 7.60E-06 6.10E-06 4.60E-06 3.00E-06 3.00E-06 3.00E-06 3.00E-06 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.580E+00 6.439E-04 0.000E+00 0.000E+00 8.516E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 9.837E-01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.516E+04 8.528E+04 1.154E+02 Percent of Total 0.00 0.00 0.00 0.00 99.86 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.86 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,7,8,9-HxCDF C:\SEV7 WIN7\1,2,3,7,8,9-HXCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8,9-HXCDF.APL Starting Depth: 195.00 cm Ending Depth: 198.80 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .0 0 E + 0 5 5 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.05E-5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.10E-5 Ligand Molecular Weight(g/mol) 0.00 1.5E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.01E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 375.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,7,8,9-HxCDF C:\SEV7 WIN7\1,2,3,7,8,9-HXCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8,9-HXCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 Layer 2 (ug/g) 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 Layer 3 (ug/g) 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 1.80E-06 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.458E+00 1.388E-03 0.000E+00 0.000E+00 1.679E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.978E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.679E+05 1.839E+05 1.597E+04 Percent of Total 0.00 0.00 0.00 0.00 91.31 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 91.31 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,7,8-PeCDD C:\SEV7 WIN7\1,2,3,7,8-PECDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8-PECDD.APL Starting Depth: 195.00 cm Ending Depth: 205.80 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 2 .0 0 E + 0 5 1 .5 0 E + 0 5 1 .0 0 E + 0 5 5 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.19E-4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.60E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 3370000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 2.70E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.38E-6 Neutral Hydrolysis 356.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,7,8-PeCDD C:\SEV7 WIN7\1,2,3,7,8-PECDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8-PECDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.80E-06 9.80E-06 9.40E-06 9.00E-06 8.70E-06 8.30E-06 7.90E-06 7.50E-06 7.20E-06 6.80E-06 Layer 2 (ug/g) 6.40E-06 6.00E-06 5.70E-06 5.30E-06 4.90E-06 4.50E-06 4.20E-06 3.80E-06 3.40E-06 3.00E-06 Layer 3 (ug/g) 2.70E-06 2.30E-06 1.90E-06 1.50E-06 1.10E-06 7.70E-07 3.90E-07 3.90E-07 3.90E-07 3.90E-07 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.564E+01 1.906E-03 0.000E+00 0.000E+00 1.682E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.408E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.682E+05 1.790E+05 1.073E+04 Percent of Total 0.01 0.00 0.00 0.00 93.99 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 94.00 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 1,2,3,7,8-PeCDF C:\SEV7 WIN7\1,2,3,7,8-PECDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8-PECDF.APL Starting Depth: 195.00 cm Ending Depth: 203.50 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I 2 .0 0 E + 0 5 1 .5 0 E + 0 5 1 .0 0 E + 0 5 5 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.40E-4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 5.00E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 4730000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 3.59E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.51E-6 Neutral Hydrolysis 340.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 1,2,3,7,8-PeCDF C:\SEV7 WIN7\1,2,3,7,8-PECDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 1,2,3,7,8-PECDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.00E-05 1.00E-05 9.80E-06 9.40E-06 9.00E-06 8.60E-06 8.20E-06 7.80E-06 7.30E-06 6.90E-06 Layer 2 (ug/g) 6.50E-06 6.10E-06 5.70E-06 5.30E-06 4.90E-06 4.50E-06 4.10E-06 3.70E-06 3.30E-06 2.90E-06 Layer 3 (ug/g) 2.50E-06 2.00E-06 1.60E-06 1.20E-06 8.20E-07 4.10E-07 5.10E-09 5.10E-09 5.10E-09 5.10E-09 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.582E+01 9.580E-04 0.000E+00 0.000E+00 1.917E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.463E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.917E+05 1.918E+05 6.082E+01 Percent of Total 0.01 0.00 0.00 0.00 99.96 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,3,4,6,7,8-HxCDF C:\SEV7 WIN7\2,3,4,6,7,8-HXCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,4,6,7,8-HXCDF.APL Starting Depth: 195.00 cm Ending Depth: 197.60 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 3 .0 0 E + 0 5 2 .0 0 E + 0 5 1 .0 0 E + 0 5 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.05E-5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.10E-5 Ligand Molecular Weight(g/mol) 0.00 2.3E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.29E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 375.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,3,4,6,7,8-HxCDF C:\SEV7 WIN7\2,3,4,6,7,8-HXCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,4,6,7,8-HXCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.10E-05 1.10E-05 1.00E-05 1.00E-05 9.60E-06 9.20E-06 8.70E-06 8.30E-06 7.90E-06 7.40E-06 Layer 2 (ug/g) 7.00E-06 6.50E-06 6.10E-06 5.70E-06 5.20E-06 4.80E-06 4.40E-06 3.90E-06 3.50E-06 3.10E-06 Layer 3 (ug/g) 2.60E-06 2.20E-06 1.80E-06 1.30E-06 8.90E-07 4.50E-07 1.50E-08 1.50E-08 1.50E-08 1.50E-08 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.803E+01 1.759E-03 0.000E+00 0.000E+00 4.937E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.631E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.940E+04 5.050E+04 1.098E+03 Percent of Total 0.04 0.00 0.00 0.00 97.78 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 97.82 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,3,4,7,8-PeCDF C:\SEV7 WIN7\2,3,4,7,8-PECDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,4,7,8-PECDF.APL Starting Depth: 195.00 cm Ending Depth: 209.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 6 .0 0 E + 0 4 4 .0 0 E + 0 4 2 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.36E-4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 8.14E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 2450000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 3.00E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.51E-6 Neutral Hydrolysis 340.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,3,4,7,8-PeCDF C:\SEV7 WIN7\2,3,4,7,8-PECDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,4,7,8-PECDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.80E-06 2.80E-06 2.70E-06 2.60E-06 2.50E-06 2.40E-06 2.30E-06 2.10E-06 2.00E-06 1.90E-06 Layer 2 (ug/g) 1.80E-06 1.70E-06 1.60E-06 1.50E-06 1.40E-06 1.30E-06 1.10E-06 1.00E-06 9.20E-07 8.10E-07 Layer 3 (ug/g) 7.00E-07 5.90E-07 4.80E-07 3.70E-07 2.60E-07 1.50E-07 3.80E-08 3.80E-08 3.80E-08 3.80E-08 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 9.952E+00 1.532E-03 0.000E+00 0.000E+00 2.103E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.830E-01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.104E+04 2.105E+04 6.462E+00 Percent of Total 0.05 0.00 0.00 0.00 99.92 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,3,7,8-TCDD C:\SEV7 WIN7\2,3,7,8-TCDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,7,8-TCDD.APL Starting Depth: 195.00 cm Ending Depth: 203.40 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 3 .0 0 E + 0 4 2 .0 0 E + 0 4 1 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.93E-5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 3.29E-5 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 4840000 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 1.43E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.72E-6 Neutral Hydrolysis 322.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,3,7,8-TCDD C:\SEV7 WIN7\2,3,7,8-TCDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,7,8-TCDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.10E-06 1.10E-06 1.10E-06 1.00E-06 9.70E-07 9.30E-07 8.90E-07 8.50E-07 8.10E-07 7.70E-07 Layer 2 (ug/g) 7.20E-07 6.80E-07 6.40E-07 6.00E-07 5.60E-07 5.20E-07 4.70E-07 4.30E-07 3.90E-07 3.50E-07 Layer 3 (ug/g) 3.10E-07 2.70E-07 2.20E-07 1.80E-07 1.40E-07 9.90E-08 5.70E-08 5.70E-08 5.70E-08 5.70E-08 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.035E+01 5.969E-03 0.000E+00 0.000E+00 3.782E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.871E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.787E+04 4.057E+04 2.695E+03 Percent of Total 0.10 0.00 0.00 0.00 93.24 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.00 93.36 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,3,7,8-TCDF C:\SEV7 WIN7\2,3,7,8-TCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,7,8-TCDF.APL Starting Depth: 195.00 cm Ending Depth: 225.30 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 6 .0 0 E + 0 4 4 .0 0 E + 0 4 2 .0 0 E + 0 4 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 4.19E-4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.46E-5 Ligand Molecular Weight(g/mol) 0.00 992000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 Air Diffusion 3.63E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.84E-6 Neutral Hydrolysis 306.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 0.00 Ligand Dissociation Constant (cm 2 /sec) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,3,7,8-TCDF C:\SEV7 WIN7\2,3,7,8-TCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,3,7,8-TCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.30E-06 2.30E-06 2.20E-06 2.10E-06 2.00E-06 1.90E-06 1.80E-06 1.70E-06 1.70E-06 1.60E-06 Layer 2 (ug/g) 1.50E-06 1.40E-06 1.30E-06 1.20E-06 1.10E-06 1.00E-06 9.20E-07 8.30E-07 7.40E-07 6.50E-07 Layer 3 (ug/g) 5.60E-07 4.70E-07 3.70E-07 2.80E-07 1.90E-07 1.00E-07 9.10E-09 9.10E-09 9.10E-09 9.10E-09 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.017E+02 1.794E-01 0.000E+00 0.000E+00 1.961E+08 0.000E+00 0.000E+00 6.560E+08 0.000E+00 0.000E+00 0.000E+00 4.473E+02 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.522E+08 8.526E+08 3.934E+05 Percent of Total 0.00 0.00 0.00 0.00 23.01 0.00 0.00 76.95 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.95 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: OCDD C:\SEV7 WIN7\OCDD.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) OCDD.APL Starting Depth: 195.00 cm Ending Depth: 195.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.37E-7 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 6.74E-6 Ligand Molecular Weight(g/mol) 0.00 7.9E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 2.95E-3 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 460.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: OCDD C:\SEV7 WIN7\OCDD.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) OCDD.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.28E-02 4.28E-02 4.12E-02 3.96E-02 3.81E-02 3.65E-02 3.49E-02 3.33E-02 3.18E-02 3.02E-02 Layer 2 (ug/g) 2.86E-02 2.70E-02 2.54E-02 2.39E-02 2.23E-02 2.07E-02 1.91E-02 1.76E-02 1.60E-02 1.44E-02 Layer 3 (ug/g) 1.28E-02 1.12E-02 9.70E-03 8.10E-03 6.50E-03 4.90E-03 3.40E-03 3.40E-03 3.40E-03 3.40E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 9.701E+00 2.418E-03 0.000E+00 0.000E+00 1.127E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.161E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.127E+07 1.140E+07 1.215E+05 Percent of Total 0.00 0.00 0.00 0.00 98.93 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 98.93 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: OCDF C:\SEV7 WIN7\OCDF.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) OCDF.APL Starting Depth: 195.00 cm Ending Depth: 195.60 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I mg 1 .5 0 E + 0 7 1 .0 0 E + 0 7 5 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.16E-6 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.88E-6 Ligand Molecular Weight(g/mol) 0.00 9.4E+7 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 8.78E-3 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 4.44 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: OCDF C:\SEV7 WIN7\OCDF.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) OCDF.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 6.40E-04 6.40E-04 6.20E-04 5.90E-04 5.70E-04 5.40E-04 5.10E-04 4.90E-04 4.60E-04 4.40E-04 Layer 2 (ug/g) 4.10E-04 3.90E-04 3.60E-04 3.40E-04 3.10E-04 2.80E-04 2.60E-04 2.30E-04 2.10E-04 1.80E-04 Layer 3 (ug/g) 1.60E-04 1.30E-04 1.10E-04 8.00E-05 5.40E-05 2.90E-05 3.30E-06 3.30E-06 3.30E-06 3.30E-06 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.653E+12 8.949E+07 0.000E+00 0.000E+00 6.499E+10 0.000E+00 0.000E+00 1.214E+14 0.000E+00 0.000E+00 0.000E+00 1.474E+03 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.231E+14 1.232E+14 1.357E+10 Percent of Total 1.34 0.00 0.00 0.00 0.05 0.00 0.00 98.59 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: ORO (C30 - C40) Aliphatics C:\SEV7 WIN7\ORO (C30-C40) ALIPHATICS.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ORO (C30-C40).APL Starting Depth: 195.00 cm Ending Depth: 195.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 1 .5 0 E + 1 4 1 .0 0 E + 1 4 5 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 7.51E-7 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.02E+3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 7.9E+9 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .100 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 309.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: ORO (C30 - C40) Aliphatics C:\SEV7 WIN7\ORO (C30-C40) ALIPHATICS.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ORO (C30-C40).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 2 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 3 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.415E+08 2.287E+04 0.000E+00 0.000E+00 3.000E+10 0.000E+00 0.000E+00 1.231E+14 0.000E+00 0.000E+00 0.000E+00 4.325E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.757E+01 1.231E+14 1.232E+14 4.674E+10 Percent of Total 0.00 0.00 0.00 0.00 0.02 0.00 0.00 99.94 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.96 Maximum leachate concentration: 1.414E-08 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: ORO (C30 - C40) Aromatics C:\SEV7 WIN7\ORO (C30-C40) AROMATICS.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ORO (C30-C40).APL Starting Depth: 195.10 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 1 .5 0 E + 1 4 1 .0 0 E + 1 4 5 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .6 0 E - 0 8 1 .4 0 E - 0 8 Concentration (mg/L) 1 .2 0 E - 0 8 1 .0 0 E - 0 8 8 .0 0 E - 0 9 6 .0 0 E - 0 9 4 .0 0 E - 0 9 2 .0 0 E - 0 9 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.78E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 8.89E-6 Ligand Molecular Weight(g/mol) 0.00 125000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 .100 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 240.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: ORO (C30 - C40) Aromatics C:\SEV7 WIN7\ORO (C30-C40) AROMATICS.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ORO (C30-C40).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 2 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 3 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.159E+13 2.652E+11 0.000E+00 0.000E+00 1.532E+12 0.000E+00 0.000E+00 5.979E+13 0.000E+00 0.000E+00 0.000E+00 8.738E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.231E+14 1.232E+14 1.471E+10 Percent of Total 49.99 0.22 0.00 0.00 1.24 0.00 0.00 48.54 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: ORO (C30 - C40) Median C:\SEV7 WIN7\ORO (C30-C40) MEDIAN.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ORO (C30-C40).APL Starting Depth: 195.00 cm Ending Depth: 196.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 1 .5 0 E + 1 4 1 .0 0 E + 1 4 5 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 8.90E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 510.0 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 3.1E+7 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .100 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 274.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: ORO (C30 - C40) Median C:\SEV7 WIN7\ORO (C30-C40) MEDIAN.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ORO (C30-C40).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 2 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 3 (ug/g) 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 2.60E+03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.768E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.776E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.768E+11 3.777E+11 8.771E+08 Percent of Total 0.00 0.00 0.00 0.00 99.76 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.77 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Antimony (Kd) C:\SEV7 WIN7\ANTIMONY.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ANTIMONY.APL Starting Depth: 380.50 cm Ending Depth: 387.50 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I 4 .0 0 E + 1 1 3 .0 0 E + 1 1 2 .0 0 E + 1 1 1 .0 0 E + 1 1 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 879.00 879.00 879.00 879.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.30E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 879.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 122.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Antimony (Kd) C:\SEV7 WIN7\ANTIMONY.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ANTIMONY.APL Sublayer Loads 1 Layer 1 (ug/g) 7.50E+00 Layer 2 (ug/g) 7.50E+00 Layer 3 (ug/g) 7.50E+00 Layer 4 (ug/g) 4.97E-01 2 3 4 5 7.50E+00 7.50E+00 7.50E+00 4.97E-01 7.50E+00 7.50E+00 7.50E+00 4.97E-01 7.50E+00 7.50E+00 7.50E+00 4.97E-01 7.50E+00 7.50E+00 7.50E+00 4.97E-01 10 7.50E+00 7.50E+00 7.50E+00 4.97E-01 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 7.50E+00 7.50E+00 7.50E+00 4.97E-01 0 .8 0 .6 .0 8 7.50E+00 7.50E+00 7.50E+00 4.97E-01 0 .9 Load Layer 1 0 .8 ug/cm2 7 7.50E+00 7.50E+00 7.50E+00 4.97E-01 1 .0 1 .0 0 6 7.50E+00 7.50E+00 7.50E+00 4.97E-01 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 1.507E+10 0.000E+00 0.000E+00 6.215E+12 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.281E+08 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.231E+12 6.301E+12 6.974E+10 Percent of Total 0.00 0.24 0.00 0.00 98.65 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 98.89 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Arsenic, Inorganic (Kd) C:\SEV7 WIN7\ARSENIC.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) ARSENIC.APL Starting Depth: 380.50 cm Ending Depth: 388.60 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t IN S O IL A IR A D S O N S O IL IN S O IL M O I 8 .0 0 E + 1 2 6 .0 0 E + 1 2 4 .0 0 E + 1 2 2 .0 0 E + 1 2 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 785.00 785.00 785.00 785.00 0.00 0.00 0.00 0.00 Latitude Spill Index 3.47E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) .772 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 785.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 77.90 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Arsenic, Inorganic (Kd) C:\SEV7 WIN7\ARSENIC.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) ARSENIC.APL Sublayer Loads 1 Layer 1 (ug/g) 1.10E+02 Layer 2 (ug/g) 1.10E+02 Layer 3 (ug/g) 1.10E+02 Layer 4 (ug/g) 2.42E+01 2 3 4 5 1.10E+02 1.10E+02 1.10E+02 2.42E+01 1.10E+02 1.10E+02 1.10E+02 2.42E+01 1.10E+02 1.10E+02 1.10E+02 2.42E+01 1.10E+02 1.10E+02 1.10E+02 2.42E+01 10 1.10E+02 1.10E+02 1.10E+02 2.42E+01 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 1.10E+02 1.10E+02 1.10E+02 2.42E+01 0 .8 0 .6 .0 8 1.10E+02 1.10E+02 1.10E+02 2.42E+01 0 .9 Load Layer 1 0 .8 ug/cm2 7 1.10E+02 1.10E+02 1.10E+02 2.42E+01 1 .0 1 .0 0 6 1.10E+02 1.10E+02 1.10E+02 2.42E+01 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.740E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.385E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.793E+10 1.747E+13 1.758E+13 1.058E+11 Percent of Total 0.00 0.00 0.00 0.00 98.99 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.39 99.40 Maximum leachate concentration: 9.979E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Barium (Kd) C:\SEV7 WIN7\BARIUM.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BARIUM.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 1 3 1 .5 0 E + 1 3 1 .0 0 E + 1 3 5 .0 0 E + 1 2 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 213.00 213.00 213.00 213.00 0.00 0.00 0.00 0.00 Latitude Spill Index 5.48E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 213.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 137.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Barium (Kd) C:\SEV7 WIN7\BARIUM.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BARIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 9.30E+01 Layer 2 (ug/g) 1.39E+02 Layer 3 (ug/g) 1.96E+02 Layer 4 (ug/g) 2.04E+02 2 3 4 5 9.30E+01 1.44E+02 2.01E+02 2.04E+02 9.30E+01 1.50E+02 2.07E+02 2.04E+02 9.87E+01 1.56E+02 2.13E+02 2.04E+02 1.04E+02 1.62E+02 2.19E+02 2.04E+02 10 1.33E+02 1.90E+02 2.30E+02 2.04E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 1.27E+02 1.84E+02 2.30E+02 2.04E+02 0 .8 0 .6 .0 8 1.22E+02 1.79E+02 2.30E+02 2.04E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 1.16E+02 1.73E+02 2.30E+02 2.04E+02 1 .0 1 .0 0 6 1.10E+02 1.67E+02 2.24E+02 2.04E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.345E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.253E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.345E+11 1.355E+11 9.058E+08 Percent of Total 0.00 0.00 0.00 0.00 99.33 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.33 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Beryllium (Kd) C:\SEV7 WIN7\BERYLLIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BERYLLIUM.APL Starting Depth: 380.50 cm Ending Depth: 387.50 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I mg 1 .5 0 E + 1 1 1 .0 0 E + 1 1 5 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 892.00 892.00 892.00 892.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.49E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 892.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 0.00 Neutral Hydrolysis 9.01 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Beryllium (Kd) C:\SEV7 WIN7\BERYLLIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BERYLLIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 8.80E-01 Layer 2 (ug/g) 1.22E+00 Layer 3 (ug/g) 1.64E+00 Layer 4 (ug/g) 1.42E+00 2 3 4 5 8.80E-01 1.26E+00 1.69E+00 1.42E+00 8.80E-01 1.30E+00 1.73E+00 1.42E+00 9.23E-01 1.35E+00 1.77E+00 1.42E+00 9.65E-01 1.39E+00 1.82E+00 1.42E+00 10 1.18E+00 1.60E+00 1.90E+00 1.42E+00 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 1.13E+00 1.56E+00 1.90E+00 1.42E+00 0 .8 0 .6 .0 8 1.09E+00 1.52E+00 1.90E+00 1.42E+00 0 .9 Load Layer 1 0 .8 ug/cm2 7 1.05E+00 1.48E+00 1.90E+00 1.42E+00 1 .0 1 .0 0 6 1.01E+00 1.43E+00 1.86E+00 1.42E+00 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.204E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.740E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.204E+11 1.212E+11 7.573E+08 Percent of Total 0.00 0.00 0.00 0.00 99.37 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.38 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Chromium (Kd) C:\SEV7 WIN7\CHROMIUM.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEXAVALENT CHROMIUM.APL Starting Depth: 380.50 cm Ending Depth: 386.50 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I mg 1 .5 0 E + 1 1 1 .0 0 E + 1 1 5 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 1050.00 1050.00 1050.00 1050.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.20E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 1050.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 52.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Chromium (Kd) C:\SEV7 WIN7\CHROMIUM.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEXAVALENT CHROMIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 3.20E+00 Layer 2 (ug/g) 2.49E+00 Layer 3 (ug/g) 1.07E+00 Layer 4 (ug/g) 1.13E+00 2 3 4 5 3.20E+00 2.35E+00 9.29E-01 1.13E+00 3.20E+00 2.21E+00 7.88E-01 1.13E+00 3.20E+00 2.06E+00 6.46E-01 1.13E+00 3.20E+00 1.92E+00 5.04E-01 1.13E+00 10 2.63E+00 1.21E+00 2.20E-01 1.13E+00 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 2.77E+00 1.36E+00 2.20E-01 1.13E+00 0 .8 0 .6 .0 8 2.92E+00 1.50E+00 2.20E-01 1.13E+00 0 .9 Load Layer 1 0 .8 ug/cm2 7 3.06E+00 1.64E+00 2.20E-01 1.13E+00 1 .0 1 .0 0 6 3.20E+00 1.78E+00 3.62E-01 1.13E+00 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 5.702E+07 1.031E+06 0.000E+00 0.000E+00 2.712E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.605E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.766E+07 2.809E+09 2.824E+09 1.453E+07 Percent of Total 2.02 0.04 0.00 0.00 96.04 0.00 0.00 0.00 0.00 0.00 0.00 0.06 0.00 0.00 0.00 0.00 1.33 99.49 Maximum leachate concentration: 4.250E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Mercury (elemental) (Kd) C:\SEV7 WIN7\MERCURY (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MERCURY.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 9 2 .0 0 E + 0 9 1 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 4 4 .0 0 E - 0 4 Concentration (mg/L) 3 .5 0 E - 0 4 3 .0 0 E - 0 4 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 70.00 70.00 70.00 70.00 0.00 0.00 0.00 0.00 Latitude Spill Index 5.62E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.08E-2 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 70.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 3.07E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.30E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Mercury (elemental) (Kd) C:\SEV7 WIN7\MERCURY (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MERCURY.APL Sublayer Loads 1 Layer 1 (ug/g) 3.30E-02 Layer 2 (ug/g) 3.30E-02 Layer 3 (ug/g) 3.30E-02 Layer 4 (ug/g) 2.80E-02 2 3 4 5 3.30E-02 3.30E-02 3.30E-02 2.80E-02 3.30E-02 3.30E-02 3.30E-02 2.80E-02 3.30E-02 3.30E-02 3.30E-02 2.80E-02 3.30E-02 3.30E-02 3.30E-02 2.80E-02 10 3.30E-02 3.30E-02 3.30E-02 2.80E-02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 3.30E-02 3.30E-02 3.30E-02 2.80E-02 0 .8 0 .6 .0 8 3.30E-02 3.30E-02 3.30E-02 2.80E-02 0 .9 Load Layer 1 0 .8 ug/cm2 7 3.30E-02 3.30E-02 3.30E-02 2.80E-02 1 .0 1 .0 0 6 3.30E-02 3.30E-02 3.30E-02 2.80E-02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.404E+10 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.242E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.516E+07 7.408E+10 7.473E+10 6.470E+08 Percent of Total 0.00 0.00 0.00 0.00 99.08 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.03 99.13 Maximum leachate concentration: 4.004E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Silver (Kd) C:\SEV7 WIN7\SILVER (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SILVER.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 1 0 6 .0 0 E + 1 0 4 .0 0 E + 1 0 2 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 4 4 .0 0 E - 0 4 Concentration (mg/L) 3 .5 0 E - 0 4 3 .0 0 E - 0 4 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 247.00 247.00 247.00 247.00 0.00 0.00 0.00 0.00 Latitude Spill Index 7.05E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 247.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 108.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Silver (Kd) C:\SEV7 WIN7\SILVER (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SILVER.APL Sublayer Loads 1 Layer 1 (ug/g) 3.50E+00 Layer 2 (ug/g) 2.41E+00 Layer 3 (ug/g) 1.05E+00 Layer 4 (ug/g) 9.50E-02 2 3 4 5 3.50E+00 2.27E+00 9.11E-01 9.50E-02 3.50E+00 2.14E+00 7.75E-01 9.50E-02 3.36E+00 2.00E+00 6.39E-01 9.50E-02 3.23E+00 1.87E+00 5.02E-01 9.50E-02 10 2.55E+00 1.18E+00 2.30E-01 9.50E-02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 2.68E+00 1.32E+00 2.30E-01 9.50E-02 0 .8 0 .6 .0 8 2.82E+00 1.46E+00 2.30E-01 9.50E-02 0 .9 Load Layer 1 0 .8 ug/cm2 7 2.95E+00 1.59E+00 2.30E-01 9.50E-02 1 .0 1 .0 0 6 3.09E+00 1.73E+00 3.66E-01 9.50E-02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.989E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.963E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.455E+13 8.494E+13 8.536E+13 4.105E+11 Percent of Total 0.00 0.00 0.00 0.00 70.17 0.00 0.00 0.00 0.00 0.00 0.00 0.58 0.00 0.00 0.00 0.00 28.77 99.52 Maximum leachate concentration: 4.772E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Starting Depth: 380.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .0 0 E + 1 4 5 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E + 0 2 Concentration (mg/L) 5 .0 0 E + 0 2 4 .0 0 E + 0 2 3 .0 0 E + 0 2 2 .0 0 E + 0 2 1 .0 0 E + 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 5.00 5.00 5.00 5.00 0.00 0.00 0.00 0.00 Latitude Spill Index 3.59E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.00 K oc Dedsorp 5.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 23.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 1.17E+03 Layer 2 (ug/g) 1.17E+03 Layer 3 (ug/g) 1.17E+03 Layer 4 (ug/g) 7.64E+02 2 3 4 5 1.17E+03 1.17E+03 1.17E+03 6.62E+02 1.17E+03 1.17E+03 1.17E+03 5.61E+02 1.17E+03 1.17E+03 1.17E+03 4.59E+02 1.17E+03 1.17E+03 1.17E+03 7.54E+02 10 1.17E+03 1.17E+03 8.65E+02 7.54E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 1.17E+03 1.17E+03 9.67E+02 7.54E+02 0 .8 0 .6 .0 8 1.17E+03 1.17E+03 1.07E+03 7.54E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 1.17E+03 1.17E+03 1.17E+03 7.54E+02 1 .0 1 .0 0 6 1.17E+03 1.17E+03 1.17E+03 7.54E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 7.853E+07 In Soil Air 3.939E+06 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.502E+08 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 4.258E+11 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 3.153E+09 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 1.698E+11 Total Output 5.991E+11 Total Input 5.991E+11 Input - Output -2.637E+07 Percent of Total 0.01 0.00 0.00 0.00 0.04 0.00 0.00 71.08 0.00 0.00 0.00 0.53 0.00 0.00 0.00 0.00 28.35 100.00 Maximum leachate concentration: 1.691E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Fluoride* DHWM+HLC from database C:\SEV7 WIN7\FLUORIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) FLUORIDE.APL Starting Depth: 390.00 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 1 1 6 .0 0 E + 1 1 4 .0 0 E + 1 1 2 .0 0 E + 1 1 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .8 0 E + 0 0 1 .6 0 E + 0 0 Concentration (mg/L) 1 .4 0 E + 0 0 1 .2 0 E + 0 0 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.69 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.10E-5 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 14.30 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .147 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 6.92E-6 Neutral Hydrolysis 38.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Fluoride* DHWM+HLC from database C:\SEV7 WIN7\FLUORIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) FLUORIDE.APL Sublayer Loads 1 Layer 1 (ug/g) 1.30E+00 Layer 2 (ug/g) 4.86E+00 Layer 3 (ug/g) 8.82E+00 Layer 4 (ug/g) 5.39E+00 2 3 4 5 1.30E+00 5.26E+00 9.22E+00 5.39E+00 1.70E+00 5.66E+00 9.62E+00 5.39E+00 2.09E+00 6.05E+00 1.00E+01 5.39E+00 2.49E+00 6.45E+00 1.04E+01 5.39E+00 10 4.47E+00 8.43E+00 1.12E+01 5.39E+00 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 4.07E+00 8.03E+00 1.12E+01 5.39E+00 0 .8 0 .6 .0 8 3.68E+00 7.64E+00 1.12E+01 5.39E+00 0 .9 Load Layer 1 0 .8 ug/cm2 7 3.28E+00 7.24E+00 1.12E+01 5.39E+00 1 .0 1 .0 0 6 2.88E+00 6.84E+00 1.08E+01 5.39E+00 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: c:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 5.455E-02 0.000E+00 0.000E+00 4.519E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.527E+12 2.527E+12 2.528E+12 6.579E+08 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 99.97 Maximum leachate concentration: 1.728E+03 mg/l Climate File: CANOGA PARK PIERCE COL c:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Nitrate (Koc) c:\sev7 win7\NITRATE-N.CHM Soil File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Starting Depth: 306.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O IL M a s s F a t e P lo t 3 .0 E + 1 2 2 .5 E + 1 2 mg 2 .0 E + 1 2 1 .5 E + 1 2 1 .0 E + 1 2 5 .0 E + 1 1 0 .0 E + 0 0 0 10 20 30 G N D W T R T O T AL 40 50 Y e a rs IN S O IL M O I 60 A D S O N S O IL Concentration (mg/L) L e a c h a t e 2 1 1 1 1 1 8 6 4 2 0 . . . . . . . . . . . 0 8 6 4 2 0 0 0 0 0 0 E E E E E E E E E E E + + + + + + + + + + + 0 0 0 0 0 0 0 0 0 0 0 70 C 80 90 100 IN S O IL A IR o n c e n t r a t io n 3 3 3 3 3 3 2 2 2 2 0 0 2 0 4 0 C Y 6 0 e a r s o n t a m i n a n t 8 0 D 1 0 0 e p t h P 1 2 0 l o t 0 - 5 0 0 2 0 4 0 6 0 Depth (cm) - 1 0 0 - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 1 2 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 10 10 10 10 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 2 Latitude Spill Index 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (µg/mL) 9.09E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.61E-5 Ligand Molecular Weight(g/mol) 0.00 Water Solubility 2.06 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 14.30 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.50E-5 Neutral Hydrolysis 62.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) c:\SEV7 WIN7\S01.OUT Chemical File: Nitrate (Koc) c:\sev7 win7\NITRATE-N.CHM EEL CC#1 (2014) Soil File: c:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL 5 92 1. 58 75 1. 1. 25 08 42 1. 1. 75 92 1. 1. 58 1. 25 42 1. 1. 08 92 75 Y e a rs Y ears L ig an d L o a d L ayer 2 1. 0. 0. 92 1. 75 1. 58 1. 42 1. 08 25 1. 1. 75 92 0. 0. 58 42 0. 0. 25 08 0 .0 58 0 .1 42 0 .2 0. 0 .3 0. 0 .4 25 0 .5 0. 0 .6 08 ug/cm2 0 .7 L ig an d L o a d L ayer 3 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 0 .8 0. 1. 0. L oad L a ye r 3 0 .9 0. 10 R a in L o a d 1 .0 L oad L a ye r 2 9 Y e a rs Y e a rs L ig a n d L o a d L a y e r 1 ug/cm2 92 08 92 1. 75 58 1. 1. 42 1. 25 08 1. 1. 92 75 0. 0. 58 0. 25 42 0. 0. 0. 08 0 .0 75 0 .2 0 .1 0. 0 .3 58 ug/cm2 ug/cm2 0 .7 Lo a d L a ye r 1 8 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 0 .9 0 .8 0 .4 7 42 1 .0 0 .6 0 .5 6 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.60E+01 4.03E+01 3.45E+01 5.80E+00 0. 4 4.60E+01 4.60E+01 4.60E+01 1.15E+01 25 3 4.60E+01 4.60E+01 4.60E+01 1.73E+01 0. 2 4.60E+01 4.60E+01 4.60E+01 2.30E+01 0. Sublayer Loads 1 Layer 1 (ug/g) 4.60E+01 Layer 2 (ug/g) 4.60E+01 Layer 3 (ug/g) 4.60E+01 Layer 4 (ug/g) 2.88E+01 L oad L a ye r 4 L ig an d L o a d L ayer 4 PROTECTION OF GROUNDWATER EVALUATION EEL RFI SITE SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 2.457E+08 3.367E+01 0.000E+00 0.000E+00 3.214E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.792E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.023E+09 1.269E+09 1.270E+09 4.858E+05 Percent of Total 19.35 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 80.61 99.96 Maximum leachate concentration: 4.467E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).APL Starting Depth: 209.90 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 5 .0 0 E - 0 1 4 .5 0 E - 0 1 Concentration (mg/L) 4 .0 0 E - 0 1 3 .5 0 E - 0 1 3 .0 0 E - 0 1 2 .5 0 E - 0 1 2 .0 0 E - 0 1 1 .5 0 E - 0 1 1 .0 0 E - 0 1 5 .0 0 E - 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.35E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.77E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 100.00 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 7.55E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.10E-6 Neutral Hydrolysis 131.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 Layer 2 (ug/g) 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 Layer 3 (ug/g) 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 2.68E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.769E+07 3.367E+01 0.000E+00 0.000E+00 3.214E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.792E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.986E+08 2.463E+08 2.464E+08 3.433E+04 Percent of Total 19.36 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 80.63 99.99 Maximum leachate concentration: 8.670E-02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).APL Starting Depth: 209.90 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 8 2 .0 0 E + 0 8 1 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .0 0 E - 0 1 9 .0 0 E - 0 2 Concentration (mg/L) 8 .0 0 E - 0 2 7 .0 0 E - 0 2 6 .0 0 E - 0 2 5 .0 0 E - 0 2 4 .0 0 E - 0 2 3 .0 0 E - 0 2 2 .0 0 E - 0 2 1 .0 0 E - 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.35E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.77E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 100.00 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 7.55E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.10E-6 Neutral Hydrolysis 131.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 Layer 2 (ug/g) 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 Layer 3 (ug/g) 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 5.20E-03 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 9.328E+05 In Soil Air 3.367E+01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 3.214E+01 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.792E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 3.823E+06 Total Output 4.756E+06 Total Input 4.738E+06 Input - Output -1.886E+04 Percent of Total 19.69 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 80.71 100.40 Maximum leachate concentration: 1.665E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).APL Starting Depth: 209.90 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .8 0 E - 0 3 1 .6 0 E - 0 3 Concentration (mg/L) 1 .4 0 E - 0 3 1 .2 0 E - 0 3 1 .0 0 E - 0 3 8 .0 0 E - 0 4 6 .0 0 E - 0 4 4 .0 0 E - 0 4 2 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.35E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.77E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 100.00 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 7.55E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.10E-6 Neutral Hydrolysis 131.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 Layer 2 (ug/g) 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 Layer 3 (ug/g) 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 1.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.35E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.77E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 100.00 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 7.55E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.10E-6 Neutral Hydrolysis 131.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 Layer 2 (ug/g) 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 Layer 3 (ug/g) 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 2.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.849E+06 In Soil Air 3.367E+01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 3.214E+01 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.792E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 7.644E+06 Total Output 9.494E+06 Total Input 9.476E+06 Input - Output -1.847E+04 Percent of Total 19.52 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 80.67 100.19 Maximum leachate concentration: 3.333E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).APL Starting Depth: 209.90 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .0 0 E + 0 7 5 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .5 0 E - 0 3 Concentration (mg/L) 3 .0 0 E - 0 3 2 .5 0 E - 0 3 2 .0 0 E - 0 3 1 .5 0 E - 0 3 1 .0 0 E - 0 3 5 .0 0 E - 0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 2.767E+06 In Soil Air 3.367E+01 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 3.214E+01 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.792E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 1.146E+07 Total Output 1.423E+07 Total Input 1.421E+07 Input - Output -2.307E+04 Percent of Total 19.47 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 80.69 100.16 Maximum leachate concentration: 5.000E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).APL Starting Depth: 209.90 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .5 0 E + 0 7 1 .0 0 E + 0 7 5 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E - 0 3 Concentration (mg/L) 5 .0 0 E - 0 3 4 .0 0 E - 0 3 3 .0 0 E - 0 3 2 .0 0 E - 0 3 1 .0 0 E - 0 3 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.35E+3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 9.77E-3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 100.00 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 7.55E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 9.10E-6 Neutral Hydrolysis 131.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Trichloroethylene C:\SEV7 WIN7\TRICHLOROETHENE (TCE).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014).APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 Layer 2 (ug/g) 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 Layer 3 (ug/g) 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 3.00E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 0.000E+00 In Soil Air 4.743E-03 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.136E+00 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.694E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 3.080E+07 Total Output 3.080E+07 Total Input 3.080E+07 Input - Output -8.119E+03 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.03 100.03 Maximum leachate concentration: 2.148E-02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Starting Depth: 220.30 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 7 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 2 .5 0 E - 0 2 Concentration (mg/L) 2 .0 0 E - 0 2 1 .5 0 E - 0 2 1 .0 0 E - 0 2 5 .0 0 E - 0 3 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.49E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.40E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 6.76 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 117.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 Layer 2 (ug/g) 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 Layer 3 (ug/g) 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 6.50E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 0.000E+00 In Soil Air 4.743E-03 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.136E+00 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.694E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 2.037E+09 Total Output 2.037E+09 Total Input 2.037E+09 Input - Output -3.304E+03 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.00 Maximum leachate concentration: 1.421E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Starting Depth: 220.30 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 9 2 .0 0 E + 0 9 1 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .6 0 E + 0 0 1 .4 0 E + 0 0 Concentration (mg/L) 1 .2 0 E + 0 0 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.49E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.40E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 6.76 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 117.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 Layer 2 (ug/g) 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 Layer 3 (ug/g) 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 4.30E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 0.000E+00 In Soil Air 4.743E-03 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.136E+00 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 0.000E+00 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 5.694E+01 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 3.128E+07 Total Output 3.128E+07 Total Input 3.127E+07 Input - Output -1.216E+04 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.04 100.04 Maximum leachate concentration: 2.181E-02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Starting Depth: 220.30 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 7 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 2 .5 0 E - 0 2 Concentration (mg/L) 2 .0 0 E - 0 2 1 .5 0 E - 0 2 1 .0 0 E - 0 2 5 .0 0 E - 0 3 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 2.49E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.40E-6 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 6.76 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 117.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Perchlorate C:\SEV7 WIN7\PERCHLORATE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) PERCHLORATE.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 Layer 2 (ug/g) 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 Layer 3 (ug/g) 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 6.60E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.359E+12 8.837E+07 0.000E+00 0.000E+00 6.417E+10 0.000E+00 0.000E+00 4.121E+13 0.000E+00 0.000E+00 0.000E+00 1.456E+03 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.263E+13 4.264E+13 4.032E+09 Percent of Total 3.19 0.00 0.00 0.00 0.15 0.00 0.00 96.65 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: DRO (C20-C30, C21-C30 Aliphatics) C:\SEV7 WIN7\DRO (C20-C30, C21-C30 ALIPHATICS).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) TPH.APL Starting Depth: 195.00 cm Ending Depth: 195.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 7.51E-7 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.02E+3 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 7.9E+9 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .100 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 309.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: DRO (C20-C30, C21-C30 Aliphatics) C:\SEV7 WIN7\DRO (C20-C30, C21-C30 ALIPHATICS).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) TPH.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 2 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 3 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.415E+08 2.287E+04 0.000E+00 0.000E+00 3.000E+10 0.000E+00 0.000E+00 4.257E+13 0.000E+00 0.000E+00 0.000E+00 4.325E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.757E+01 4.260E+13 4.264E+13 3.684E+10 Percent of Total 0.00 0.00 0.00 0.00 0.07 0.00 0.00 99.84 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.91 Maximum leachate concentration: 1.414E-08 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: DRO (C20-C30, C21-C30 Aromatics) C:\SEV7 WIN7\DRO (C20-C30, C21-C30 AROMATICS).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) TPH.APL Starting Depth: 195.10 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .6 0 E - 0 8 1 .4 0 E - 0 8 Concentration (mg/L) 1 .2 0 E - 0 8 1 .0 0 E - 0 8 8 .0 0 E - 0 9 6 .0 0 E - 0 9 4 .0 0 E - 0 9 2 .0 0 E - 0 9 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.78E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 8.89E-6 Ligand Molecular Weight(g/mol) 0.00 125000 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 .100 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 240.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: DRO (C20-C30, C21-C30 Aromatics) C:\SEV7 WIN7\DRO (C20-C30, C21-C30 AROMATICS).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) TPH.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 2 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 3 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 2.132E+13 2.652E+11 0.000E+00 0.000E+00 1.532E+12 0.000E+00 0.000E+00 1.951E+13 0.000E+00 0.000E+00 0.000E+00 8.738E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.263E+13 4.264E+13 7.271E+09 Percent of Total 50.00 0.62 0.00 0.00 3.59 0.00 0.00 45.77 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.98 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: DRO (C20-C30, C21-C30 Median) C:\SEV7 WIN7\DRO (C20-C30, C21-C30 MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) TPH.APL Starting Depth: 195.00 cm Ending Depth: 196.70 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VO L T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I mg 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 8.90E-3 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 510.0 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 3.1E+7 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .100 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 274.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: DRO (C20-C30, C21-C30 Median) C:\SEV7 WIN7\DRO (C20-C30, C21-C30 MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) TPH.APL Sublayer Loads 1 2 3 4 5 6 7 8 9 10 Layer 1 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 2 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 3 (ug/g) 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 9.00E+02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load Layer 3 R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 8 0 .0 .0 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 0 0 .9 Load Layer 1 0 .8 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.937E+01 7.671E-06 0.000E+00 0.000E+00 4.938E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.810E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.279E+09 1.279E+09 1.279E+09 -5.273E+04 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.00 Maximum leachate concentration: 5.706E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Starting Depth: 209.80 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E -0 1 Concentration (mg/L) 5 .0 0 E -0 1 4 .0 0 E -0 1 3 .0 0 E -0 1 2 .0 0 E -0 1 1 .0 0 E -0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp 2.68E-09 Ligand Molecular Weight (g/mol) 0.00 185.00 K oc Dedsorp 0.00 K d Dedsorp (g/mole) (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 4.60E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 1.17E-6 Neutral Hydrolysis 221.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 55.3 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 Layer 2 (ug/g) 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 Layer 3 (ug/g) 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 2.70E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 8.221E+01 7.671E-06 0.000E+00 0.000E+00 4.938E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.810E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.515E+09 1.515E+09 1.516E+09 5.569E+04 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.00 100.00 Maximum leachate concentration: 6.763E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Starting Depth: 209.80 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 0 9 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 8 .0 0 E -0 1 7 .0 0 E -0 1 Concentration (mg/L) 6 .0 0 E -0 1 5 .0 0 E -0 1 4 .0 0 E -0 1 3 .0 0 E -0 1 2 .0 0 E -0 1 1 .0 0 E -0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp 2.68E-09 Ligand Molecular Weight (g/mol) 0.00 185.00 K oc Dedsorp 0.00 K d Dedsorp (g/mole) (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 4.60E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 1.17E-6 Neutral Hydrolysis 221.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 55.3 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 Layer 2 (ug/g) 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 Layer 3 (ug/g) 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 3.20E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 7.194E+01 7.671E-06 0.000E+00 0.000E+00 4.938E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.810E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.326E+09 1.326E+09 1.327E+09 4.558E+05 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 99.97 Maximum leachate concentration: 5.918E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Starting Depth: 209.80 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .5 0 E + 0 9 1 .0 0 E + 0 9 5 .0 0 E + 0 8 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 7 .0 0 E -0 1 Concentration (mg/L) 6 .0 0 E -0 1 5 .0 0 E -0 1 4 .0 0 E -0 1 3 .0 0 E -0 1 2 .0 0 E -0 1 1 .0 0 E -0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp 2.68E-09 Ligand Molecular Weight (g/mol) 0.00 185.00 K oc Dedsorp 0.00 K d Dedsorp (g/mole) (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 4.60E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 1.17E-6 Neutral Hydrolysis 221.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 55.3 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: 2,4-Dichlorophenoxybutyric Acid C:\SEV7 WIN7\2,4-DICHLOROPHENOXYBUTYRIC ACID 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) 2,4-DB.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 Layer 2 (ug/g) 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 Layer 3 (ug/g) 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.005E+03 7.149E-06 0.000E+00 0.000E+00 1.639E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.885E+10 1.885E+10 1.886E+10 6.478E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 99.97 Maximum leachate concentration: 1.295E+01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Starting Depth: 216.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 1 0 1 .5 0 E + 1 0 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .4 0 E + 0 1 Concentration (mg/L) 1 .2 0 E + 0 1 1 .0 0 E + 0 1 8 .0 0 E + 0 0 6 .0 0 E + 0 0 4 .0 0 E + 0 0 2 .0 0 E + 0 0 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp 2.11E-09 Ligand Molecular Weight (g/mol) 0.00 51.80 K oc Dedsorp 0.00 K d Dedsorp (g/mole) (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 5.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.42E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 825.0 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 Layer 2 (ug/g) 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 Layer 3 (ug/g) 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 3.98E-01 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 2.374E+03 7.149E-06 0.000E+00 0.000E+00 1.639E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.453E+10 4.453E+10 4.454E+10 9.464E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.98 99.98 Maximum leachate concentration: 3.061E+01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Starting Depth: 216.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 1 0 4 .0 0 E + 1 0 2 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .5 0 E + 0 1 Concentration (mg/L) 3 .0 0 E + 0 1 2 .5 0 E + 0 1 2 .0 0 E + 0 1 1 .5 0 E + 0 1 1 .0 0 E + 0 1 5 .0 0 E + 0 0 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp 2.11E-09 Ligand Molecular Weight (g/mol) 0.00 51.80 K oc Dedsorp 0.00 K d Dedsorp (g/mole) (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 5.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.42E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 825.0 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 Layer 2 (ug/g) 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 Layer 3 (ug/g) 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 9.40E-01 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.008E+03 7.149E-06 0.000E+00 0.000E+00 1.639E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.890E+10 1.890E+10 1.890E+10 -1.279E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.01 100.01 Maximum leachate concentration: 1.299E+01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Starting Depth: 216.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 1 0 1 .5 0 E + 1 0 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .4 0 E + 0 1 Concentration (mg/L) 1 .2 0 E + 0 1 1 .0 0 E + 0 1 8 .0 0 E + 0 0 6 .0 0 E + 0 0 4 .0 0 E + 0 0 2 .0 0 E + 0 0 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp 2.11E-09 Ligand Molecular Weight (g/mol) 0.00 51.80 K oc Dedsorp 0.00 K d Dedsorp (g/mole) (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 5.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.42E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 825.0 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: MCPA C:\SEV7 WIN7\MCPA 2014.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MCPA.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 Layer 2 (ug/g) 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 Layer 3 (ug/g) 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 3.99E-01 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.010E+01 4.720E-02 0.000E+00 0.000E+00 1.966E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.149E+03 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.222E+06 6.243E+06 6.159E+06 -8.456E+04 Percent of Total 0.00 0.00 0.00 0.00 0.32 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 101.03 101.37 Maximum leachate concentration: 3.457E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Starting Depth: 198.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 6 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .0 0 E -0 4 3 .5 0 E -0 4 Concentration (mg/L) 3 .0 0 E -0 4 2 .5 0 E -0 4 2 .0 0 E -0 4 1 .5 0 E -0 4 1 .0 0 E -0 4 5 .0 0 E -0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 6.90E-7 Ligand Molecular Weight (g/mol) 0.00 3080.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 2.10E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.37E-6 Neutral Hydrolysis 291.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 4.52 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 2 (ug/g) 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 3 (ug/g) 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.676E+02 4.768E-02 0.000E+00 0.000E+00 1.986E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.161E+03 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.462E+07 3.465E+07 3.459E+07 -6.083E+04 Percent of Total 0.00 0.00 0.00 0.00 0.06 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 100.11 100.18 Maximum leachate concentration: 1.942E-03 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Starting Depth: 198.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 4 .0 0 E + 0 7 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 2 .5 0 E -0 3 Concentration (mg/L) 2 .0 0 E -0 3 1 .5 0 E -0 3 1 .0 0 E -0 3 5 .0 0 E -0 4 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 6.90E-7 Ligand Molecular Weight (g/mol) 0.00 3080.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 2.10E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.37E-6 Neutral Hydrolysis 291.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 4.52 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 Layer 2 (ug/g) 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 Layer 3 (ug/g) 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 7.30E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.239E+01 4.720E-02 0.000E+00 0.000E+00 1.966E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.149E+03 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.696E+06 6.717E+06 6.633E+06 -8.482E+04 Percent of Total 0.00 0.00 0.00 0.00 0.30 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 100.96 101.28 Maximum leachate concentration: 3.722E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Starting Depth: 198.60 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 6 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .0 0 E -0 4 3 .5 0 E -0 4 Concentration (mg/L) 3 .0 0 E -0 4 2 .5 0 E -0 4 2 .0 0 E -0 4 1 .5 0 E -0 4 1 .0 0 E -0 4 5 .0 0 E -0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 6.90E-7 Ligand Molecular Weight (g/mol) 0.00 3080.00 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 2.10E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 7.37E-6 Neutral Hydrolysis 291.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 4.52 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: beta-Hexachlorocyclohexane [beta-Lindane](Median C:\SEV7 WIN7\BETA-BHC (MEDIAN).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BETA-BHC.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 Layer 2 (ug/g) 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 Layer 3 (ug/g) 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 1.40E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 7.252E+03 1.514E+03 0.000E+00 0.000E+00 5.323E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.171E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.891E+05 5.863E+06 5.686E+06 -1.774E+05 Percent of Total 0.13 0.03 0.00 0.00 93.63 0.00 0.00 0.00 0.00 0.00 0.00 0.73 0.00 0.00 0.00 0.00 8.60 103.12 Maximum leachate concentration: 2.461E-05 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Starting Depth: 195.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 6 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .0 0 E -0 5 Concentration (mg/L) 2 .5 0 E -0 5 2 .0 0 E -0 5 1 .5 0 E -0 5 1 .0 0 E -0 5 5 .0 0 E -0 6 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 6.10E-4 Ligand Molecular Weight (g/mol) 0.00 23000.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 1.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.15E-6 Neutral Hydrolysis 373.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 .180 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 Layer 2 (ug/g) 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 Layer 3 (ug/g) 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 3.262E+04 7.117E+03 0.000E+00 0.000E+00 2.503E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.960E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.377E+06 2.764E+07 2.748E+07 -1.645E+05 Percent of Total 0.12 0.03 0.00 0.00 91.09 0.00 0.00 0.00 0.00 0.00 0.00 0.71 0.00 0.00 0.00 0.00 8.65 100.60 Maximum leachate concentration: 1.187E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Starting Depth: 195.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .4 0 E -0 4 Concentration (mg/L) 1 .2 0 E -0 4 1 .0 0 E -0 4 8 .0 0 E -0 5 6 .0 0 E -0 5 4 .0 0 E -0 5 2 .0 0 E -0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 6.10E-4 Ligand Molecular Weight (g/mol) 0.00 23000.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 1.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.15E-6 Neutral Hydrolysis 373.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 .180 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 Layer 2 (ug/g) 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 Layer 3 (ug/g) 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 5.80E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 7.804E+03 1.635E+03 0.000E+00 0.000E+00 5.751E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.506E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.297E+05 6.335E+06 6.159E+06 -1.769E+05 Percent of Total 0.13 0.03 0.00 0.00 93.39 0.00 0.00 0.00 0.00 0.00 0.00 0.73 0.00 0.00 0.00 0.00 8.60 102.87 Maximum leachate concentration: 2.663E-05 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Starting Depth: 195.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 6 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .0 0 E -0 5 Concentration (mg/L) 2 .5 0 E -0 5 2 .0 0 E -0 5 1 .5 0 E -0 5 1 .0 0 E -0 5 5 .0 0 E -0 6 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 6.10E-4 Ligand Molecular Weight (g/mol) 0.00 23000.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 1.68E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 5.15E-6 Neutral Hydrolysis 373.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 .180 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor C:\SEV7 WIN7\HEPTACHLOR.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 2 (ug/g) 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 3 (ug/g) 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 1.30E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.710E+02 2.113E+01 0.000E+00 0.000E+00 3.256E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.738E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.030E+06 5.324E+06 5.212E+06 -1.125E+05 Percent of Total 0.00 0.00 0.00 0.00 62.48 0.00 0.00 0.00 0.00 0.00 0.00 0.72 0.00 0.00 0.00 0.00 38.96 102.16 Maximum leachate concentration: 6.080E-05 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Starting Depth: 195.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 7 .0 0 E -0 5 Concentration (mg/L) 6 .0 0 E -0 5 5 .0 0 E -0 5 4 .0 0 E -0 5 3 .0 0 E -0 5 2 .0 0 E -0 5 1 .0 0 E -0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 9.50E-6 Ligand Molecular Weight (g/mol) 0.00 15700.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 2.19E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 389.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 .200 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 Layer 2 (ug/g) 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 Layer 3 (ug/g) 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 1.10E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 6.868E+02 8.745E+01 0.000E+00 0.000E+00 1.347E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.547E+05 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.726E+06 2.236E+07 2.227E+07 -9.029E+04 Percent of Total 0.00 0.00 0.00 0.00 60.52 0.00 0.00 0.00 0.00 0.00 0.00 0.69 0.00 0.00 0.00 0.00 39.18 100.41 Maximum leachate concentration: 2.594E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Starting Depth: 195.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 7 2 .0 0 E + 0 7 1 .0 0 E + 0 7 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 3 .0 0 E -0 4 Concentration (mg/L) 2 .5 0 E -0 4 2 .0 0 E -0 4 1 .5 0 E -0 4 1 .0 0 E -0 4 5 .0 0 E -0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 9.50E-6 Ligand Molecular Weight (g/mol) 0.00 15700.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 2.19E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 389.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 .200 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 2 (ug/g) 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 3 (ug/g) 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 4.70E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 1.853E+02 2.296E+01 0.000E+00 0.000E+00 3.538E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.063E+04 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.216E+06 5.795E+06 5.686E+06 -1.096E+05 Percent of Total 0.00 0.00 0.00 0.00 62.24 0.00 0.00 0.00 0.00 0.00 0.00 0.71 0.00 0.00 0.00 0.00 38.97 101.93 Maximum leachate concentration: 6.629E-05 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Starting Depth: 195.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t V O L T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 0 6 6 .0 0 E + 0 6 4 .0 0 E + 0 6 2 .0 0 E + 0 6 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 7 .0 0 E -0 5 Concentration (mg/L) 6 .0 0 E -0 5 5 .0 0 E -0 5 4 .0 0 E -0 5 3 .0 0 E -0 5 2 .0 0 E -0 5 1 .0 0 E -0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n t a m 6 0 Y e a r s in a n t D e p t h 8 0 1 0 0 P lo t 0 0 2 0 4 0 6 0 - 5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 (M 3-atm/mol) Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) 9.50E-6 Ligand Molecular Weight (g/mol) 0.00 15700.0 K oc Dedsorp 0.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 0.00 Ligand Dissociation Constant Air Diffusion (cm 2/sec) 2.19E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 4.23E-6 Neutral Hydrolysis 389.00 Acid Hydrolysis (L/mol/day) 0.00 0.00 (g/mol) Molecular Weight 1 0.00 (g/mole) Valence 1.15E+8 1.23E+5 34.2 .200 Moles Ligand / Moles Chemical (µg/mL) 0.21 Application Parameters cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (L/mol/day) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Heptachlor Epoxide C:\SEV7 WIN7\HEPTACHLOR EPOXIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) HEPTACHLOR EPOXIDE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 Layer 2 (ug/g) 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 Layer 3 (ug/g) 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 1.20E-04 Layer 4 (ug/g) 1 .0 1 .0 0 .7 Load La R a in L o a d 0 .6 ug/cm2 ug/cm2 0 .8 0 .6 0 .4 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 08 L ig a n d L Layer 3 0 .5 0 .4 0 .2 0. 0 .9 Load Layer 1 0 .8 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 58 75 0. 0. 42 0. 0. 08 0. 25 0 .0 Y ears Y ears 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load La Load La ug/cm2 0 .6 L ig a n d L Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y ears Y ears 92 1. 75 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0. 08 0. 75 92 1. 1. 58 1. 42 1. 25 1. 08 1. 92 0. 75 0. 58 0. 42 0. 25 0 .0 0. 08 0 .0 L ig a n d L Layer 4 0 .5 0 .4 0. ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.861E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.622E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.793E+10 1.868E+13 1.883E+13 1.410E+11 Percent of Total 0.00 0.00 0.00 0.00 98.87 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.36 99.25 Maximum leachate concentration: 9.979E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Barium (Kd) C:\SEV7 WIN7\BARIUM.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BARIUM.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 1 3 1 .5 0 E + 1 3 1 .0 0 E + 1 3 5 .0 0 E + 1 2 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 213.00 213.00 213.00 213.00 0.00 0.00 0.00 0.00 Latitude Spill Index 5.48E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 213.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 137.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Barium (Kd) C:\SEV7 WIN7\BARIUM.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BARIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 2.04E+02 Layer 2 (ug/g) 2.04E+02 Layer 3 (ug/g) 2.04E+02 Layer 4 (ug/g) 2.04E+02 2 3 4 5 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2.04E+02 10 2.04E+02 2.04E+02 2.04E+02 2.04E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 2.04E+02 2.04E+02 2.04E+02 2.04E+02 0 .8 0 .6 .0 8 2.04E+02 2.04E+02 2.04E+02 2.04E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 2.04E+02 2.04E+02 2.04E+02 2.04E+02 1 .0 1 .0 0 6 2.04E+02 2.04E+02 2.04E+02 2.04E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.981E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.855E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.793E+10 1.988E+13 2.007E+13 1.812E+11 Percent of Total 0.00 0.00 0.00 0.00 98.74 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.34 99.10 Maximum leachate concentration: 9.979E-01 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Barium (Kd) C:\SEV7 WIN7\BARIUM.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) BARIUM.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 1 3 2 .0 0 E + 1 3 1 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 213.00 213.00 213.00 213.00 0.00 0.00 0.00 0.00 Latitude Spill Index 5.48E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 213.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 137.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Barium (Kd) C:\SEV7 WIN7\BARIUM.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) BARIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 2.30E+02 Layer 2 (ug/g) 2.30E+02 Layer 3 (ug/g) 2.30E+02 Layer 4 (ug/g) 2.04E+02 2 3 4 5 2.30E+02 2.30E+02 2.30E+02 2.04E+02 2.30E+02 2.30E+02 2.30E+02 2.04E+02 2.30E+02 2.30E+02 2.30E+02 2.04E+02 2.30E+02 2.30E+02 2.30E+02 2.04E+02 10 2.30E+02 2.30E+02 2.30E+02 2.04E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 2.30E+02 2.30E+02 2.30E+02 2.04E+02 0 .8 0 .6 .0 8 2.30E+02 2.30E+02 2.30E+02 2.04E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 2.30E+02 2.30E+02 2.30E+02 2.04E+02 1 .0 1 .0 0 6 2.30E+02 2.30E+02 2.30E+02 2.04E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.002E+10 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.332E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.002E+10 4.019E+10 1.600E+08 Percent of Total 0.00 0.00 0.00 0.00 99.60 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 99.60 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Cadmium (Water) (Kd) C:\SEV7 WIN7\CADMIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) CADMIUM.APL Starting Depth: 380.50 cm Ending Depth: 389.30 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I mg 6 .0 0 E + 1 0 4 .0 0 E + 1 0 2 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 711.00 711.00 711.00 711.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.23E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 711.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 112.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Cadmium (Water) (Kd) C:\SEV7 WIN7\CADMIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) CADMIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 4.35E-01 Layer 2 (ug/g) 4.35E-01 Layer 3 (ug/g) 4.35E-01 Layer 4 (ug/g) 4.35E-01 2 3 4 5 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 4.35E-01 10 4.35E-01 4.35E-01 4.35E-01 4.35E-01 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 4.35E-01 4.35E-01 4.35E-01 4.35E-01 0 .8 0 .6 .0 8 4.35E-01 4.35E-01 4.35E-01 4.35E-01 0 .9 Load Layer 1 0 .8 ug/cm2 7 4.35E-01 4.35E-01 4.35E-01 4.35E-01 1 .0 1 .0 0 6 4.35E-01 4.35E-01 4.35E-01 4.35E-01 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.178E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.269E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.178E+11 2.186E+11 7.728E+08 Percent of Total 0.00 0.00 0.00 0.00 99.64 0.00 0.00 0.00 0.00 0.00 0.00 0.01 0.00 0.00 0.00 0.00 0.00 99.65 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Cadmium (Water) (Kd) C:\SEV7 WIN7\CADMIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) CADMIUM.APL Starting Depth: 380.50 cm Ending Depth: 389.30 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I mg 3 .0 0 E + 1 1 2 .0 0 E + 1 1 1 .0 0 E + 1 1 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 711.00 711.00 711.00 711.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.23E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 711.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 112.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Cadmium (Water) (Kd) C:\SEV7 WIN7\CADMIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) CADMIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 4.20E+00 Layer 2 (ug/g) 4.20E+00 Layer 3 (ug/g) 4.20E+00 Layer 4 (ug/g) 4.35E-01 2 3 4 5 4.20E+00 4.20E+00 4.20E+00 4.35E-01 4.20E+00 4.20E+00 4.20E+00 4.35E-01 4.20E+00 4.20E+00 4.20E+00 4.35E-01 4.20E+00 4.20E+00 4.20E+00 4.35E-01 10 4.20E+00 4.20E+00 4.20E+00 4.35E-01 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 4.20E+00 4.20E+00 4.20E+00 4.35E-01 0 .8 0 .6 .0 8 4.20E+00 4.20E+00 4.20E+00 4.35E-01 0 .9 Load Layer 1 0 .8 ug/cm2 7 4.20E+00 4.20E+00 4.20E+00 4.35E-01 1 .0 1 .0 0 6 4.20E+00 4.20E+00 4.20E+00 4.35E-01 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.658E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.273E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.658E+13 6.680E+13 2.143E+11 Percent of Total 0.00 0.00 0.00 0.00 99.67 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.68 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Manganese (Kd) C:\SEV7 WIN7\MANGANESE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MANGANESE.APL Starting Depth: 380.50 cm Ending Depth: 388.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I 8 .0 0 E + 1 3 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 843.00 843.00 843.00 843.00 0.00 0.00 0.00 0.00 Latitude Spill Index 8.72E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 843.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 54.90 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Manganese (Kd) C:\SEV7 WIN7\MANGANESE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MANGANESE.APL Sublayer Loads 1 Layer 1 (ug/g) 7.23E+02 Layer 2 (ug/g) 7.23E+02 Layer 3 (ug/g) 7.23E+02 Layer 4 (ug/g) 7.23E+02 2 3 4 5 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 7.23E+02 10 7.23E+02 7.23E+02 7.23E+02 7.23E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 7.23E+02 7.23E+02 7.23E+02 7.23E+02 0 .8 0 .6 .0 8 7.23E+02 7.23E+02 7.23E+02 7.23E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 7.23E+02 7.23E+02 7.23E+02 7.23E+02 1 .0 1 .0 0 6 7.23E+02 7.23E+02 7.23E+02 7.23E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.392E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.633E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 7.392E+13 7.457E+13 6.410E+11 Percent of Total 0.00 0.00 0.00 0.00 99.14 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.14 Maximum leachate concentration: 0.000E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Manganese (Kd) C:\SEV7 WIN7\MANGANESE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MANGANESE.APL Starting Depth: 380.50 cm Ending Depth: 388.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I 8 .0 0 E + 1 3 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .2 0 E + 0 0 Concentration (mg/L) 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 843.00 843.00 843.00 843.00 0.00 0.00 0.00 0.00 Latitude Spill Index 8.72E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 843.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 54.90 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Manganese (Kd) C:\SEV7 WIN7\MANGANESE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MANGANESE.APL Sublayer Loads 1 Layer 1 (ug/g) 8.87E+02 Layer 2 (ug/g) 8.87E+02 Layer 3 (ug/g) 8.87E+02 Layer 4 (ug/g) 7.23E+02 2 3 4 5 8.87E+02 8.87E+02 8.87E+02 7.23E+02 8.87E+02 8.87E+02 8.87E+02 7.23E+02 8.87E+02 8.87E+02 8.87E+02 7.23E+02 8.87E+02 8.87E+02 8.87E+02 7.23E+02 10 8.87E+02 8.87E+02 8.87E+02 7.23E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 8.87E+02 8.87E+02 8.87E+02 7.23E+02 0 .8 0 .6 .0 8 8.87E+02 8.87E+02 8.87E+02 7.23E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 8.87E+02 8.87E+02 8.87E+02 7.23E+02 1 .0 1 .0 0 6 8.87E+02 8.87E+02 8.87E+02 7.23E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 4.838E+07 9.455E+05 0.000E+00 0.000E+00 2.485E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.471E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.766E+07 2.573E+09 2.587E+09 1.351E+07 Percent of Total 1.87 0.04 0.00 0.00 96.06 0.00 0.00 0.00 0.00 0.00 0.00 0.06 0.00 0.00 0.00 0.00 1.46 99.48 Maximum leachate concentration: 4.250E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Mercury (elemental) (Kd) C:\SEV7 WIN7\MERCURY (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MERCURY.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 9 2 .0 0 E + 0 9 1 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 4 4 .0 0 E - 0 4 Concentration (mg/L) 3 .5 0 E - 0 4 3 .0 0 E - 0 4 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 70.00 70.00 70.00 70.00 0.00 0.00 0.00 0.00 Latitude Spill Index 5.62E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.08E-2 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 70.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 3.07E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.30E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Mercury (elemental) (Kd) C:\SEV7 WIN7\MERCURY (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MERCURY.APL Sublayer Loads 1 Layer 1 (ug/g) 2.80E-02 Layer 2 (ug/g) 2.80E-02 Layer 3 (ug/g) 2.80E-02 Layer 4 (ug/g) 2.80E-02 2 3 4 5 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2.80E-02 10 2.80E-02 2.80E-02 2.80E-02 2.80E-02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 2.80E-02 2.80E-02 2.80E-02 2.80E-02 0 .8 0 .6 .0 8 2.80E-02 2.80E-02 2.80E-02 2.80E-02 0 .9 Load Layer 1 0 .8 ug/cm2 7 2.80E-02 2.80E-02 2.80E-02 2.80E-02 1 .0 1 .0 0 6 2.80E-02 2.80E-02 2.80E-02 2.80E-02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 5.702E+07 1.031E+06 0.000E+00 0.000E+00 2.712E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.605E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.766E+07 2.809E+09 2.824E+09 1.453E+07 Percent of Total 2.02 0.04 0.00 0.00 96.04 0.00 0.00 0.00 0.00 0.00 0.00 0.06 0.00 0.00 0.00 0.00 1.33 99.49 Maximum leachate concentration: 4.250E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Mercury (elemental) (Kd) C:\SEV7 WIN7\MERCURY (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) MERCURY.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 3 .0 0 E + 0 9 2 .0 0 E + 0 9 1 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 4 4 .0 0 E - 0 4 Concentration (mg/L) 3 .5 0 E - 0 4 3 .0 0 E - 0 4 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 70.00 70.00 70.00 70.00 0.00 0.00 0.00 0.00 Latitude Spill Index 5.62E-2 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 1.08E-2 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 70.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 Air Diffusion (cm 2 /sec) 3.07E-2 Base Hydrolysis Rate(L/mol/day) 0.00 Water Diffusion (cm 2/sec) 6.30E-6 Neutral Hydrolysis 201.00 Acid Hydrolysis (L/mol/day) 0.00 (L/mol/day) 0.00 Molecular Weight 1 (µg/g)/(µg/mL) (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Mercury (elemental) (Kd) C:\SEV7 WIN7\MERCURY (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) MERCURY.APL Sublayer Loads 1 Layer 1 (ug/g) 3.30E-02 Layer 2 (ug/g) 3.30E-02 Layer 3 (ug/g) 3.30E-02 Layer 4 (ug/g) 2.80E-02 2 3 4 5 3.30E-02 3.30E-02 3.30E-02 2.80E-02 3.30E-02 3.30E-02 3.30E-02 2.80E-02 3.30E-02 3.30E-02 3.30E-02 2.80E-02 3.30E-02 3.30E-02 3.30E-02 2.80E-02 10 3.30E-02 3.30E-02 3.30E-02 2.80E-02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 3.30E-02 3.30E-02 3.30E-02 2.80E-02 0 .8 0 .6 .0 8 3.30E-02 3.30E-02 3.30E-02 2.80E-02 0 .9 Load Layer 1 0 .8 ug/cm2 7 3.30E-02 3.30E-02 3.30E-02 2.80E-02 1 .0 1 .0 0 6 3.30E-02 3.30E-02 3.30E-02 2.80E-02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 8.714E+09 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.462E+06 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.516E+07 8.740E+09 8.777E+09 3.618E+07 Percent of Total 0.00 0.00 0.00 0.00 99.28 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.29 99.59 Maximum leachate concentration: 4.004E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Silver (Kd) C:\SEV7 WIN7\SILVER (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SILVER.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .0 0 E + 1 0 5 .0 0 E + 0 9 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 4 4 .0 0 E - 0 4 Concentration (mg/L) 3 .5 0 E - 0 4 3 .0 0 E - 0 4 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 247.00 247.00 247.00 247.00 0.00 0.00 0.00 0.00 Latitude Spill Index 7.05E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 247.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 108.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Silver (Kd) C:\SEV7 WIN7\SILVER (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SILVER.APL Sublayer Loads 1 Layer 1 (ug/g) 9.50E-02 Layer 2 (ug/g) 9.50E-02 Layer 3 (ug/g) 9.50E-02 Layer 4 (ug/g) 9.50E-02 2 3 4 5 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 9.50E-02 10 9.50E-02 9.50E-02 9.50E-02 9.50E-02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 9.50E-02 9.50E-02 9.50E-02 9.50E-02 0 .8 0 .6 .0 8 9.50E-02 9.50E-02 9.50E-02 9.50E-02 0 .9 Load Layer 1 0 .8 ug/cm2 7 9.50E-02 9.50E-02 9.50E-02 9.50E-02 1 .0 1 .0 0 6 9.50E-02 9.50E-02 9.50E-02 9.50E-02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 1.680E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.819E+07 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.516E+07 1.681E+11 1.701E+11 1.982E+09 Percent of Total 0.00 0.00 0.00 0.00 98.80 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.00 0.00 0.00 0.00 0.01 98.83 Maximum leachate concentration: 4.004E-04 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Silver (Kd) C:\SEV7 WIN7\SILVER (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SILVER.APL Starting Depth: 380.50 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 2 .0 0 E + 1 1 1 .5 0 E + 1 1 1 .0 0 E + 1 1 5 .0 0 E + 1 0 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E - 0 4 4 .0 0 E - 0 4 Concentration (mg/L) 3 .5 0 E - 0 4 3 .0 0 E - 0 4 2 .5 0 E - 0 4 2 .0 0 E - 0 4 1 .5 0 E - 0 4 1 .0 0 E - 0 4 5 .0 0 E - 0 5 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 247.00 247.00 247.00 247.00 0.00 0.00 0.00 0.00 Latitude Spill Index 7.05E+4 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 0.00 K oc Dedsorp 247.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 0.00 Neutral Hydrolysis 108.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Silver (Kd) C:\SEV7 WIN7\SILVER (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SILVER.APL Sublayer Loads 1 Layer 1 (ug/g) 3.50E+00 Layer 2 (ug/g) 3.50E+00 Layer 3 (ug/g) 3.50E+00 Layer 4 (ug/g) 9.50E-02 2 3 4 5 3.50E+00 3.50E+00 3.50E+00 9.50E-02 3.50E+00 3.50E+00 3.50E+00 9.50E-02 3.50E+00 3.50E+00 3.50E+00 9.50E-02 3.50E+00 3.50E+00 3.50E+00 9.50E-02 10 3.50E+00 3.50E+00 3.50E+00 9.50E-02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 3.50E+00 3.50E+00 3.50E+00 9.50E-02 0 .8 0 .6 .0 8 3.50E+00 3.50E+00 3.50E+00 9.50E-02 0 .9 Load Layer 1 0 .8 ug/cm2 7 3.50E+00 3.50E+00 3.50E+00 9.50E-02 1 .0 1 .0 0 6 3.50E+00 3.50E+00 3.50E+00 9.50E-02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.561E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.780E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.330E+13 6.929E+13 6.966E+13 3.695E+11 Percent of Total 0.00 0.00 0.00 0.00 65.48 0.00 0.00 0.00 0.00 0.00 0.00 0.54 0.00 0.00 0.00 0.00 33.45 99.47 Maximum leachate concentration: 4.024E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Starting Depth: 380.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 1 3 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E + 0 2 4 .0 0 E + 0 2 Concentration (mg/L) 3 .5 0 E + 0 2 3 .0 0 E + 0 2 2 .5 0 E + 0 2 2 .0 0 E + 0 2 1 .5 0 E + 0 2 1 .0 0 E + 0 2 5 .0 0 E + 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 5.00 5.00 5.00 5.00 0.00 0.00 0.00 0.00 Latitude Spill Index 3.59E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.00 K oc Dedsorp 5.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 23.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 7.54E+02 Layer 2 (ug/g) 7.54E+02 Layer 3 (ug/g) 7.54E+02 Layer 4 (ug/g) 7.54E+02 2 3 4 5 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 7.54E+02 10 7.54E+02 7.54E+02 7.54E+02 7.54E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 7.54E+02 7.54E+02 7.54E+02 7.54E+02 0 .8 0 .6 .0 8 7.54E+02 7.54E+02 7.54E+02 7.54E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 7.54E+02 7.54E+02 7.54E+02 7.54E+02 1 .0 1 .0 0 6 7.54E+02 7.54E+02 7.54E+02 7.54E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.284E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.208E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.556E+13 8.893E+13 8.937E+13 4.345E+11 Percent of Total 0.00 0.00 0.00 0.00 70.32 0.00 0.00 0.00 0.00 0.00 0.00 0.58 0.00 0.00 0.00 0.00 28.61 99.51 Maximum leachate concentration: 5.082E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Starting Depth: 380.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL mg 1 .0 0 E + 1 4 5 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 6 .0 0 E + 0 2 Concentration (mg/L) 5 .0 0 E + 0 2 4 .0 0 E + 0 2 3 .0 0 E + 0 2 2 .0 0 E + 0 2 1 .0 0 E + 0 2 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 5.00 5.00 5.00 5.00 0.00 0.00 0.00 0.00 Latitude Spill Index 3.59E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.00 K oc Dedsorp 5.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 23.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 1.17E+03 Layer 2 (ug/g) 1.17E+03 Layer 3 (ug/g) 1.17E+03 Layer 4 (ug/g) 7.54E+02 2 3 4 5 1.17E+03 1.17E+03 1.17E+03 7.54E+02 1.17E+03 1.17E+03 1.17E+03 7.54E+02 1.17E+03 1.17E+03 1.17E+03 7.54E+02 1.17E+03 1.17E+03 1.17E+03 7.54E+02 10 1.17E+03 1.17E+03 1.17E+03 7.54E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 1.17E+03 1.17E+03 1.17E+03 7.54E+02 0 .8 0 .6 .0 8 1.17E+03 1.17E+03 1.17E+03 7.54E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 1.17E+03 1.17E+03 1.17E+03 7.54E+02 1 .0 1 .0 0 6 1.17E+03 1.17E+03 1.17E+03 7.54E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.565E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.784E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.330E+13 6.933E+13 6.971E+13 3.725E+11 Percent of Total 0.00 0.00 0.00 0.00 65.49 0.00 0.00 0.00 0.00 0.00 0.00 0.54 0.00 0.00 0.00 0.00 33.43 99.47 Maximum leachate concentration: 4.024E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Starting Depth: 380.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 1 3 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E + 0 2 4 .0 0 E + 0 2 Concentration (mg/L) 3 .5 0 E + 0 2 3 .0 0 E + 0 2 2 .5 0 E + 0 2 2 .0 0 E + 0 2 1 .5 0 E + 0 2 1 .0 0 E + 0 2 5 .0 0 E + 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 5.00 5.00 5.00 5.00 0.00 0.00 0.00 0.00 Latitude Spill Index 3.59E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.00 K oc Dedsorp 5.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 23.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 7.55E+02 Layer 2 (ug/g) 7.55E+02 Layer 3 (ug/g) 7.55E+02 Layer 4 (ug/g) 7.54E+02 2 3 4 5 7.55E+02 7.55E+02 7.55E+02 7.54E+02 7.55E+02 7.55E+02 7.55E+02 7.54E+02 7.55E+02 7.55E+02 7.55E+02 7.54E+02 7.55E+02 7.55E+02 7.55E+02 7.54E+02 10 7.55E+02 7.55E+02 7.55E+02 7.54E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 7.55E+02 7.55E+02 7.55E+02 7.54E+02 0 .8 0 .6 .0 8 7.55E+02 7.55E+02 7.55E+02 7.54E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 7.55E+02 7.55E+02 7.55E+02 7.54E+02 1 .0 1 .0 0 6 7.55E+02 7.55E+02 7.55E+02 7.54E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.569E+13 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 3.787E+11 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.331E+13 6.938E+13 6.976E+13 3.744E+11 Percent of Total 0.00 0.00 0.00 0.00 65.50 0.00 0.00 0.00 0.00 0.00 0.00 0.54 0.00 0.00 0.00 0.00 33.42 99.46 Maximum leachate concentration: 4.027E+02 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Starting Depth: 380.70 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm mg S E S O I L M a s s F a te P lo t A D S O N S O IL IN S O IL M O I G ND W T R T O T AL 8 .0 0 E + 1 3 6 .0 0 E + 1 3 4 .0 0 E + 1 3 2 .0 0 E + 1 3 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 4 .5 0 E + 0 2 4 .0 0 E + 0 2 Concentration (mg/L) 3 .5 0 E + 0 2 3 .0 0 E + 0 2 2 .5 0 E + 0 2 2 .0 0 E + 0 2 1 .5 0 E + 0 2 1 .0 0 E + 0 2 5 .0 0 E + 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t - 3 8 0 0 2 0 4 0 6 0 - 3 8 2 Depth (cm) - 3 8 4 - 3 8 6 - 3 8 8 - 3 9 0 - 3 9 2 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 5.00 5.00 5.00 5.00 0.00 0.00 0.00 0.00 Latitude Spill Index 3.59E+5 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 0.00 Ligand Molecular Weight(g/mol) 0.00 0.00 K oc Dedsorp 5.00 K d Dedsorp (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 1.00E-5 Neutral Hydrolysis 23.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Sodium (Kd) C:\SEV7 WIN7\SODIUM (KD).CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) SODIUM.APL Sublayer Loads 1 Layer 1 (ug/g) 7.56E+02 Layer 2 (ug/g) 7.56E+02 Layer 3 (ug/g) 7.56E+02 Layer 4 (ug/g) 7.54E+02 2 3 4 5 7.56E+02 7.56E+02 7.56E+02 7.54E+02 7.56E+02 7.56E+02 7.56E+02 7.54E+02 7.56E+02 7.56E+02 7.56E+02 7.54E+02 7.56E+02 7.56E+02 7.56E+02 7.54E+02 10 7.56E+02 7.56E+02 7.56E+02 7.54E+02 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 7.56E+02 7.56E+02 7.56E+02 7.54E+02 0 .8 0 .6 .0 8 7.56E+02 7.56E+02 7.56E+02 7.54E+02 0 .9 Load Layer 1 0 .8 ug/cm2 7 7.56E+02 7.56E+02 7.56E+02 7.54E+02 1 .0 1 .0 0 6 7.56E+02 7.56E+02 7.56E+02 7.54E+02 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.410E+08 In Soil Air 3.151E+06 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.001E+08 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 3.250E+11 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 2.522E+09 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 1.698E+11 Total Output 4.977E+11 Total Input 4.977E+11 Input - Output -1.843E+07 Percent of Total 0.03 0.00 0.00 0.00 0.04 0.00 0.00 65.31 0.00 0.00 0.00 0.51 0.00 0.00 0.00 0.00 34.12 100.00 Maximum leachate concentration: 1.691E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Fluoride* DHWM+HLC from database C:\SEV7 WIN7\FLUORIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) FLUORIDE.APL Starting Depth: 390.00 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 6 .0 0 E + 1 1 4 .0 0 E + 1 1 2 .0 0 E + 1 1 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .8 0 E + 0 0 1 .6 0 E + 0 0 Concentration (mg/L) 1 .4 0 E + 0 0 1 .2 0 E + 0 0 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.69 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.10E-5 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 14.30 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .147 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 6.92E-6 Neutral Hydrolysis 38.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Fluoride* DHWM+HLC from database C:\SEV7 WIN7\FLUORIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) FLUORIDE.APL Sublayer Loads 1 Layer 1 (ug/g) 5.39E+00 Layer 2 (ug/g) 5.39E+00 Layer 3 (ug/g) 5.39E+00 Layer 4 (ug/g) 5.39E+00 2 3 4 5 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 5.39E+00 10 5.39E+00 5.39E+00 5.39E+00 5.39E+00 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 5.39E+00 5.39E+00 5.39E+00 5.39E+00 0 .8 0 .6 .0 8 5.39E+00 5.39E+00 5.39E+00 5.39E+00 0 .9 Load Layer 1 0 .8 ug/cm2 7 5.39E+00 5.39E+00 5.39E+00 5.39E+00 1 .0 1 .0 0 6 5.39E+00 5.39E+00 5.39E+00 5.39E+00 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: C:\SEV7 WIN7\S01.OUT SESOIL Pollutant Process Mass (µg) Volatilized 1.864E+08 In Soil Air 3.939E+06 Sur. Runoff 0.000E+00 In Washld 0.000E+00 Ads On Soil 2.502E+08 Hydrol Soil 0.000E+00 Degrad Soil 0.000E+00 Pure Phase 5.997E+11 Complexed 0.000E+00 Immobile CEC 0.000E+00 Hydrol CEC 0.000E+00 In Soil Moi 3.153E+09 Hydrol Mois 0.000E+00 Degrad Mois 0.000E+00 Other Trans 0.000E+00 Other Sinks 0.000E+00 Gwr. Runoff 1.698E+11 Total Output 7.731E+11 Total Input 7.731E+11 Input - Output -9.426E+07 Percent of Total 0.02 0.00 0.00 0.00 0.03 0.00 0.00 77.58 0.00 0.00 0.00 0.41 0.00 0.00 0.00 0.00 21.97 100.01 Maximum leachate concentration: 1.691E+00 mg/l Climate File: CANOGA PARK PIERCE COL C:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Fluoride* DHWM+HLC from database C:\SEV7 WIN7\FLUORIDE.CHM Soil File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) C:\SEV7 WIN7\EEL CC#1 (2014) FLUORIDE.APL Starting Depth: 390.00 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O I L M a s s F a te P lo t VOL T O T AL IN S O IL A IR A D S O N S O IL P URE P HAS E IN S O IL M O I G ND W T R T O T AL mg 1 .0 0 E + 1 2 5 .0 0 E + 1 1 0 .0 0 E + 0 0 0 10 20 30 40 50 60 Y e a rs 70 L e a c h a te 80 90 100 C o n c e n tr a tio n 1 .8 0 E + 0 0 1 .6 0 E + 0 0 Concentration (mg/L) 1 .4 0 E + 0 0 1 .2 0 E + 0 0 1 .0 0 E + 0 0 8 .0 0 E - 0 1 6 .0 0 E - 0 1 4 .0 0 E - 0 1 2 .0 0 E - 0 1 0 .0 0 E + 0 0 0 2 0 4 0 C o n ta m 6 0 Y e a r s in a n t D e p t h P 8 0 1 0 0 lo t 0 0 2 0 4 0 6 0 -5 0 - 1 0 0 Depth (cm) - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 Solid Liquid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate µg/g mEq 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm 10 10 10 10 feet 50.0 50.0 100.0 190.0 1.64 1.64 3.28 6.23 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 Latitude Spill Index 1.69 Moles Ligand / Moles Chemical 0.00 (M 3-atm/mol) 2.10E-5 Ligand Molecular Weight(g/mol) 0.00 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) 14.30 K oc Dedsorp 0.00 K d Dedsorp K d Adsorp (µg/g)/(µg/mL) Application Parameters 2 7.50 7.50 7.50 7.00 (µg/mL) Water Solubility 2.06 (g/mole) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 1.00 0.00E+00 0.00E+00 Soil pH Air Diffusion (cm 2 /sec) Water Diffusion (cm 2/sec) Molecular Weight 1 (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 .147 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 (L/mol/day) 0.00 6.92E-6 Neutral Hydrolysis 38.00 Acid Hydrolysis (g/mol) Output File: EEL CC#1 (2014) C:\SEV7 WIN7\S01.OUT Chemical File: Fluoride* DHWM+HLC from database C:\SEV7 WIN7\FLUORIDE.CHM EEL CC#1 (2014) Soil File: C:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: C:\SEV7 WIN7\EEL CC#1 (2014) FLUORIDE.APL Sublayer Loads 1 Layer 1 (ug/g) 1.12E+01 Layer 2 (ug/g) 1.12E+01 Layer 3 (ug/g) 1.12E+01 Layer 4 (ug/g) 5.39E+00 2 3 4 5 1.12E+01 1.12E+01 1.12E+01 5.39E+00 1.12E+01 1.12E+01 1.12E+01 5.39E+00 1.12E+01 1.12E+01 1.12E+01 5.39E+00 1.12E+01 1.12E+01 1.12E+01 5.39E+00 10 1.12E+01 1.12E+01 1.12E+01 5.39E+00 0 .7 Load Layer 3 R a in L o a d ug/cm2 0 .6 0 .4 L ig a n d L o a d Layer 3 0 .5 0 .4 0 .2 L ig a n d L o a d Layer 1 0 .3 75 0 .2 0 .1 1. 33 92 1. 0. 0. 50 0 .0 8 9 1.12E+01 1.12E+01 1.12E+01 5.39E+00 0 .8 0 .6 .0 8 1.12E+01 1.12E+01 1.12E+01 5.39E+00 0 .9 Load Layer 1 0 .8 ug/cm2 7 1.12E+01 1.12E+01 1.12E+01 5.39E+00 1 .0 1 .0 0 6 1.12E+01 1.12E+01 1.12E+01 5.39E+00 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 .0 2 1 0 .9 5 .7 8 0 .5 0 .4 0 .2 5 8 0 .0 0 2 0 .0 Y e a rs Y e ars 1 .0 1 .0 0 .9 0 .9 0 .8 0 .8 0 .7 0 .7 Load Layer 2 Load Layer 4 ug/cm2 0 .6 L ig a n d L o a d Layer 2 0 .5 0 .4 0 .3 0 .3 0 .2 0 .2 0 .1 0 .1 Y e ars Y e ars 2 .9 1 1 .7 5 8 1 .5 2 1 .4 5 1 .2 8 1 .0 2 0 .9 5 .7 8 0 0 .5 2 .4 0 .2 5 8 0 0 .0 2 .9 1 .7 5 8 1 1 .5 2 .4 5 1 1 .2 8 1 .0 2 0 .9 5 0 .7 8 .5 0 0 .4 5 .2 0 .0 2 0 .0 8 0 .0 L ig a n d L o a d Layer 4 0 .5 0 .4 0 ug/cm2 0 .6 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: c:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 5.455E-02 0.000E+00 0.000E+00 4.519E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 2.084E+10 2.084E+10 2.085E+10 5.763E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.97 99.97 Maximum leachate concentration: 1.472E+01 mg/l Climate File: CANOGA PARK PIERCE COL c:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM Soil File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Starting Depth: 219.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O IL M a s s F a t e P lo t 2 .5 E + 1 0 mg 2 .0 E + 1 0 1 .5 E + 1 0 1 .0 E + 1 0 5 .0 E + 0 9 0 .0 E + 0 0 0 10 20 30 G N D W TR TO TAL 40 50 Y e a rs IN S O IL M O I 60 A D S O N S O IL Concentration (mg/L) L e a c h a t e 1 .6 E + 0 1 1 .4 E + 0 1 1 .2 E + 0 1 1 .0 E + 0 1 8 .0 E + 0 0 6 .0 E + 0 0 4 .0 E + 0 0 2 .0 E + 0 0 0 .0 E + 0 0 0 2 0 4 0 C 70 Y C 90 100 IN S O IL A IR o n c e n t r a t i o n 6 0 e a r s o n t a m 80 i n a n t 8 0 D 1 0 0 e p t h P 1 2 0 l o t 0 - 5 0 0 2 0 4 0 6 0 Depth (cm) - 1 0 0 - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 1 2 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 10 10 10 10 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index (µg/mL) (M 3-atm/mol) 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp Application Parameters 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 0.00 1.61E-5 Ligand Molecular Weight (g/mol) 0.00 14.30 K oc Dedsorp 0.00 K d Dedsorp (g/mole) Air Diffusion (cm 2/sec) Water Diffusion (cm 2/sec) Molecular Weight 1 9.09E+4 Moles Ligand / Moles Chemical (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 0.00 1.50E-5 Neutral Hydrolysis 62.00 Acid Hydrolysis (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) c:\SEV7 WIN7\S01.OUT Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM EEL CC#1 (2014) Soil File: c:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 Layer 2 (ug/g) 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 Layer 3 (ug/g) 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 4.40E-01 Layer 4 (ug/g) L oad L ayer 3 L ig a n d L o a d L a ye r 2 92 1. 58 75 1. 1. 25 42 1. 75 92 1. 1. 58 1. 25 42 1. 1. 08 92 Y e a rs Y ears L oad L ayer 2 1. 0. 92 1. 75 1. 58 1. 42 1. 08 25 1. 1. 75 92 0. 0. 58 42 0. 0. 0. 25 0 .0 75 0 .1 0. 0 .2 58 0 .3 42 0 .4 0. 0 .5 0. 0 .6 25 ug/cm2 0 .7 0. 0 .8 08 0 .9 L ig a n d L o a d L a ye r 3 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 1 .0 08 08 R a in L o a d L ig a n d L o a d L a ye r 1 0. 1. 92 75 Y e a rs Y e a rs Lo a d La ye r 1 ug/cm2 1. 0. 0. 08 92 1. 75 58 1. 1. 1. 42 25 1. 1. 08 92 75 0. 0. 58 0. 25 42 0. 0. 0. 08 0 .0 0. 0 .2 0 .1 58 0 .3 42 0 .4 0. 0 .6 0 .5 25 ug/cm2 ug/cm2 0 .7 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 0 .9 0 .8 0. 1 .0 L oad L ayer 4 L ig a n d L o a d L a ye r 4 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: c:\SEV7 WIN7\S01.OUT SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 5.455E-02 0.000E+00 0.000E+00 4.519E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 4.737E+10 4.737E+10 4.738E+10 6.661E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 99.99 Maximum leachate concentration: 3.346E+01 mg/l Climate File: CANOGA PARK PIERCE COL c:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM Soil File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Starting Depth: 219.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O IL M a s s F a t e P lo t 5 .0 E + 1 0 mg 4 .0 E + 1 0 3 .0 E + 1 0 2 .0 E + 1 0 1 .0 E + 1 0 0 .0 E + 0 0 0 10 20 30 G N D W TR TO TAL 40 50 Y e a rs IN S O IL M O I 60 A D S O N S O IL Concentration (mg/L) L e a c h a t e 4 .0 E + 0 1 3 .5 E + 0 1 3 .0 E + 0 1 2 .5 E + 0 1 2 .0 E + 0 1 1 .5 E + 0 1 1 .0 E + 0 1 5 .0 E + 0 0 0 .0 E + 0 0 0 2 0 4 0 C 70 Y C 90 100 IN S O IL A IR o n c e n t r a t i o n 6 0 e a r s o n t a m 80 i n a n t 8 0 D 1 0 0 e p t h P 1 2 0 l o t 0 - 5 0 0 2 0 4 0 6 0 Depth (cm) - 1 0 0 - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 1 2 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 10 10 10 10 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index (µg/mL) (M 3-atm/mol) 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp Application Parameters 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 0.00 1.61E-5 Ligand Molecular Weight (g/mol) 0.00 14.30 K oc Dedsorp 0.00 K d Dedsorp (g/mole) Air Diffusion (cm 2/sec) Water Diffusion (cm 2/sec) Molecular Weight 1 9.09E+4 Moles Ligand / Moles Chemical (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 0.00 1.50E-5 Neutral Hydrolysis 62.00 Acid Hydrolysis (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) c:\SEV7 WIN7\S01.OUT Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM EEL CC#1 (2014) Soil File: c:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 Layer 2 (ug/g) 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 Layer 3 (ug/g) 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 1.00E+00 Layer 4 (ug/g) L oad L ayer 3 L ig a n d L o a d L a ye r 2 92 1. 58 75 1. 1. 25 42 1. 75 92 1. 1. 58 1. 25 42 1. 1. 08 92 Y e a rs Y ears L oad L ayer 2 1. 0. 92 1. 75 1. 58 1. 42 1. 08 25 1. 1. 75 92 0. 0. 58 42 0. 0. 0. 25 0 .0 75 0 .1 0. 0 .2 58 0 .3 42 0 .4 0. 0 .5 0. 0 .6 25 ug/cm2 0 .7 0. 0 .8 08 0 .9 L ig a n d L o a d L a ye r 3 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 1 .0 08 08 R a in L o a d L ig a n d L o a d L a ye r 1 0. 1. 92 75 Y e a rs Y e a rs Lo a d La ye r 1 ug/cm2 1. 0. 0. 08 92 1. 75 58 1. 1. 1. 42 25 1. 1. 08 92 75 0. 0. 58 0. 25 42 0. 0. 0. 08 0 .0 0. 0 .2 0 .1 58 0 .3 42 0 .4 0. 0 .6 0 .5 25 ug/cm2 ug/cm2 0 .7 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 0 .9 0 .8 0. 1 .0 L oad L ayer 4 L ig a n d L o a d L a ye r 4 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: c:\SEV7 WIN7\S01.OUT mg SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 5.455E-02 0.000E+00 0.000E+00 4.519E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.158E+10 6.158E+10 6.159E+10 3.905E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 99.99 Maximum leachate concentration: 4.351E+01 mg/l Climate File: CANOGA PARK PIERCE COL c:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM Soil File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Starting Depth: 219.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O IL M a s s F a t e P lo t 7 .0 E + 1 0 6 .0 E + 1 0 5 .0 E + 1 0 4 .0 E + 1 0 3 .0 E + 1 0 2 .0 E + 1 0 1 .0 E + 1 0 0 .0 E + 0 0 0 10 20 30 G N D W TR TO TAL 40 50 Y e a rs IN S O IL M O I 60 A D S O N S O IL Concentration (mg/L) L e a c h a t e 5 4 4 3 3 2 2 1 1 5 0 . . . . . . . . . . . 0 5 0 5 0 5 0 5 0 0 0 E E E E E E E E E E E + + + + + + + + + + + 0 0 0 0 0 0 0 0 0 0 0 70 C 80 90 100 IN S O IL A IR o n c e n t r a t i o n 1 1 1 1 1 1 1 1 1 0 0 0 2 0 4 0 C Y 6 0 e a r s o n t a m i n a n t 8 0 D 1 0 0 e p t h P 1 2 0 l o t 0 - 5 0 0 2 0 4 0 6 0 Depth (cm) - 1 0 0 - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 1 2 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 10 10 10 10 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index (µg/mL) (M 3-atm/mol) 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp Application Parameters 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 0.00 1.61E-5 Ligand Molecular Weight (g/mol) 0.00 14.30 K oc Dedsorp 0.00 K d Dedsorp (g/mole) Air Diffusion (cm 2/sec) Water Diffusion (cm 2/sec) Molecular Weight 1 9.09E+4 Moles Ligand / Moles Chemical (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 0.00 1.50E-5 Neutral Hydrolysis 62.00 Acid Hydrolysis (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) c:\SEV7 WIN7\S01.OUT Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM EEL CC#1 (2014) Soil File: c:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 Layer 2 (ug/g) 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 Layer 3 (ug/g) 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 1.30E+00 Layer 4 (ug/g) L oad L ayer 3 L ig a n d L o a d L a ye r 2 92 1. 58 75 1. 1. 25 42 1. 75 92 1. 1. 58 1. 25 42 1. 1. 08 92 Y e a rs Y ears L oad L ayer 2 1. 0. 92 1. 75 1. 58 1. 42 1. 08 25 1. 1. 75 92 0. 0. 58 42 0. 0. 0. 25 0 .0 75 0 .1 0. 0 .2 58 0 .3 42 0 .4 0. 0 .5 0. 0 .6 25 ug/cm2 0 .7 0. 0 .8 08 0 .9 L ig a n d L o a d L a ye r 3 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 1 .0 08 08 R a in L o a d L ig a n d L o a d L a ye r 1 0. 1. 92 75 Y e a rs Y e a rs Lo a d La ye r 1 ug/cm2 1. 0. 0. 08 92 1. 75 58 1. 1. 1. 42 25 1. 1. 08 92 75 0. 0. 58 0. 25 42 0. 0. 0. 08 0 .0 0. 0 .2 0 .1 58 0 .3 42 0 .4 0. 0 .6 0 .5 25 ug/cm2 ug/cm2 0 .7 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 0 .9 0 .8 0. 1 .0 L oad L ayer 4 L ig a n d L o a d L a ye r 4 SESOIL Pollutant Cycle Report Scenario Description: EEL CC#1 (2014) SESOIL Output File: c:\SEV7 WIN7\S01.OUT mg SESOIL Process Volatilized In Soil Air Sur. Runoff In Washld Ads On Soil Hydrol Soil Degrad Soil Pure Phase Complexed Immobile CEC Hydrol CEC In Soil Moi Hydrol Mois Degrad Mois Other Trans Other Sinks Gwr. Runoff Total Output Total Input Input - Output Pollutant Mass (µg) 0.000E+00 5.455E-02 0.000E+00 0.000E+00 4.519E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 0.000E+00 5.694E+01 0.000E+00 0.000E+00 0.000E+00 0.000E+00 6.632E+10 6.632E+10 6.633E+10 7.864E+06 Percent of Total 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 99.99 99.99 Maximum leachate concentration: 4.684E+01 mg/l Climate File: CANOGA PARK PIERCE COL c:\SEV7 WIN7\CANOGA PARK PERCE COL.CLM Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM Soil File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014).SOI Application File: EEL CC#1 (2014) c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Starting Depth: 219.40 cm Ending Depth: 390.00 cm Total Depth: 390.00 cm S E S O IL M a s s F a t e P lo t 7 .0 E + 1 0 6 .0 E + 1 0 5 .0 E + 1 0 4 .0 E + 1 0 3 .0 E + 1 0 2 .0 E + 1 0 1 .0 E + 1 0 0 .0 E + 0 0 0 10 20 30 G N D W TR TO TAL 40 50 Y e a rs IN S O IL M O I 60 A D S O N S O IL Concentration (mg/L) L e a c h a t e 5 4 4 3 3 2 2 1 1 5 0 . . . . . . . . . . . 0 5 0 5 0 5 0 5 0 0 0 E E E E E E E E E E E + + + + + + + + + + + 0 0 0 0 0 0 0 0 0 0 0 70 C 80 90 100 IN S O IL A IR o n c e n t r a t i o n 1 1 1 1 1 1 1 1 1 0 0 0 2 0 4 0 C Y 6 0 e a r s o n t a m i n a n t 8 0 D 1 0 0 e p t h P 1 2 0 l o t 0 - 5 0 0 2 0 4 0 6 0 Depth (cm) - 1 0 0 - 1 5 0 - 2 0 0 - 2 5 0 - 3 0 0 - 3 5 0 - 4 0 0 - 4 5 0 Y e a r s 8 0 1 0 0 1 2 0 SESOIL Profile and Load Report Number Layer of SubNo. Layers 1 2 3 4 10 10 10 10 Liquid Solid Intrinsic Organic Adsorption Cation Freundlich Phase Phase Carbon Coefficient Exchange Exponent Degradation Degradation Permeability Content Capacity Rate Rate mEq µg/g 1/day 1/day cm 2 percent 100 g soil unitless µg/mL Thickness cm feet 1.64 1.64 3.28 6.23 50.0 50.0 100.0 190.0 1.00E-8 1.00E-8 1.00E-8 3.80E-10 0.02 0.02 0.02 0.02 0.00 0.00 0.00 0.00 Water Solubility 2.06 2 Latitude Spill Index (µg/mL) (M 3-atm/mol) 0.21 Henry's Law 7.70 K oc Adsorp (µg/g)/(µg/mL) K d Adsorp Application Parameters 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 0.00E+00 7.50 7.50 7.50 7.00 0.00 1.61E-5 Ligand Molecular Weight (g/mol) 0.00 14.30 K oc Dedsorp 0.00 K d Dedsorp (g/mole) Air Diffusion (cm 2/sec) Water Diffusion (cm 2/sec) Molecular Weight 1 9.09E+4 Moles Ligand / Moles Chemical (µg/g)/(µg/mL) Valence 1.15E+8 1.23E+5 34.2 cm ft 2 degrees 1.00 1.00 1.00 1.00 pH Chemical Parameters Soil Parameters Bulk Density (g/cm 3 ) Effective Porosity (fraction) Soil Pore Disconnectedness Area 0.00 0.00 0.00 0.00 Soil pH (µg/g)/(µg/mL) 0.00 (µg/g)/(µg/mL) 0.00 0.00 Ligand Dissociation Constant 0.00 0.00 Base Hydrolysis Rate(L/mol/day) 0.00 (L/mol/day) 0.00 0.00 1.50E-5 Neutral Hydrolysis 62.00 Acid Hydrolysis (g/mol) (L/mol/day) Output File: EEL CC#1 (2014) c:\SEV7 WIN7\S01.OUT Chemical File: Nitrate (Koc) c:\SEV7 WIN7\NITRATE-N.CHM EEL CC#1 (2014) Soil File: c:\SEV7 WIN7\EEL CC#1 (2014).SOI EEL CC#1 (2014) Application File: c:\SEV7 WIN7\EEL CC#1 (2014) 1,1-DCE.APL Sublayer Loads 6 7 8 9 10 1 2 3 4 5 Layer 1 (ug/g) 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 Layer 2 (ug/g) 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 Layer 3 (ug/g) 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 1.40E+00 Layer 4 (ug/g) L oad L ayer 3 L ig a n d L o a d L a ye r 2 92 1. 58 75 1. 1. 25 42 1. 75 92 1. 1. 58 1. 25 42 1. 1. 08 92 Y e a rs Y ears L oad L ayer 2 1. 0. 92 1. 75 1. 58 1. 42 1. 08 25 1. 1. 75 92 0. 0. 58 42 0. 0. 0. 25 0 .0 75 0 .1 0. 0 .2 58 0 .3 42 0 .4 0. 0 .5 0. 0 .6 25 ug/cm2 0 .7 0. 0 .8 08 0 .9 L ig a n d L o a d L a ye r 3 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 1 .0 08 08 R a in L o a d L ig a n d L o a d L a ye r 1 0. 1. 92 75 Y e a rs Y e a rs Lo a d La ye r 1 ug/cm2 1. 0. 0. 08 92 1. 75 58 1. 1. 1. 42 25 1. 1. 08 92 75 0. 0. 58 0. 25 42 0. 0. 0. 08 0 .0 0. 0 .2 0 .1 58 0 .3 42 0 .4 0. 0 .6 0 .5 25 ug/cm2 ug/cm2 0 .7 1 .0 0 .9 0 .8 0 .7 0 .6 0 .5 0 .4 0 .3 0 .2 0 .1 0 .0 0. 0 .9 0 .8 0. 1 .0 L oad L ayer 4 L ig a n d L o a d L a ye r 4 Appendix Groundwater Source Zone and Plume Characterization for EEL RFI Site Draft APPENDIX D: GROUNDWATER SOURCE ZONE AND PLUME CHARACTERIZATION ENVIRONMENTAL EFFECTS LABORATORY RFI SITE SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CALIFORNIA Prepared For: THE BOEING COMPANY Prepared By: MWH 2121 N. California Blvd., Suite 600 Walnut Creek, CA 94596 June 10, 2015 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory RFI Site DRAFT June 2015 EXECUTIVE SUMMARY This Appendix D: Groundwater Source Zone and Plume Characterization for the Environmental Effects Laboratory (EEL) Resource Conservation and Recovery Act (RCRA) Facility Investigation (RFI) site located within Subarea 5/9 South at Santa Susana Field Laboratory (SSFL) in Ventura County, California, was completed in accordance with the Comprehensive Data Quality Objectives (DQOs) for Groundwater and Seeps developed for SSFL (CH2M HILL, 2013) to support completion of Boeing’s RFI and subsequent transition to the corrective measures study (CMS). The objective of this report is to document methodologies used in performing the groundwater source zone and plume characterization evaluation for the EEL RFI site and provide detailed results of the evaluation. The evaluation was performed to identify site-related chemicals that have impacted underlying groundwater and to evaluate their nature and extent. The groundwater source zone and plume characterization evaluation involved a comprehensive review and evaluation of groundwater data from wells interpreted to be potentially impacted by sources at the EEL RFI site. Based on evaluation of the source zone, nature and extent, and fate and transport of chemicals in groundwater at the EEL RFI site, the following chemicals are recommended for CMS assessment in groundwater: • trichloroethene • cis-1,2-dichloroethene The following chemicals are recommended for additional sampling at the specified wells: • cadmium – at PZ-050 • manganese – at PZ-050 • diesel range organics – at PZ-050 and ES-30 ES-1 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 TABLE OF CONTENTS Section Page EXECUTIVE SUMMARY .................................................................................................... ES-1 D.1 INTRODUCTION ................................................................................................................ D-1 D.2 GROUNDWATER EVALUATION APPROACH..................................................................... D-2 D.3 FIELD WORK ................................................................................................................... D-4 D.4 SOURCE ZONE EVALUATION ........................................................................................... D-5 D.5 NATURE AND EXTENT ..................................................................................................... D-6 D.6 FATE AND TRANSPORT .................................................................................................... D-7 D.7 RECOMMENDATIONS ....................................................................................................... D-9 REFERENCES........................................................................................................................ D-11 i Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory LIST OF FIGURES Figure D-1 Figure D-2 Figure D-3 Summary Evaluation of Groundwater Assessment at EEL Groundwater Sensitivity Analysis Approach Statistical Trend Analysis Evaluation Methodology LIST OF TABLES Table D-1 Table D-2 Table D-3 Summary of Groundwater Results for EEL Groundwater Results for Chemicals Sourced from Vadose Zone Statistical Trend Analysis Results LIST OF ATTACHMENTS Attachment D-1 Attachment D-2 Estimate of Transport Distances based on Darcy Flux EEL Concentration Trend Graphs ii DRAFT June 2015 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory LIST OF ABBREVIATIONS AND ACRONYMS CC chemical use area cluster CMS corrective measures study COCs chemicals of concern CUA chemical use area DCE dichloroethene DNAPL dense non-aqueous phase liquid DQOs data quality objectives DRO diesel range organics EEL Environmental Effects Laboratory GCLs groundwater characterization levels (equivalent to GCVs) GCVs groundwater comparison values m/s meters per second NFA no further action PAHs polycyclic aromatic hydrocarbons PCBs polychlorinated biphenyl RCRA Resource Conservation and Recovery Act RFI RCRA facility investigation SSFL Santa Susana Field Laboratory STL-IV Systems Test Laboratory IV STP-III Area III Sewage Treatment Plant SVOCs semi-volatile organic compounds TCE trichloroethene TPH total petroleum hydrocarbons VOCs volatile organic compounds iii DRAFT June 2015 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory D.1 DRAFT June 2015 Introduction This Appendix D: Groundwater Source Zone and Plume Characterization for the Environmental Effects Laboratory (EEL) Resource Conservation and Recovery Act (RCRA) Facility Investigation (RFI) site located within Subarea 5/9 South at Santa Susana Field Laboratory (SSFL) in Ventura County, California, was completed in accordance with the Comprehensive Data Quality Objectives (DQOs) for Groundwater and Seeps developed for SSFL (CH2M HILL, 2013) to support completion of Boeing’s RFI and subsequent transition to the corrective measures study (CMS). The objective of this report is to document methodologies used in performing the groundwater source zone and plume characterization evaluation for the EEL RFI site and provide detailed results of the evaluation. The evaluation was performed to identify site-related chemicals that have impacted underlying groundwater and to evaluate their nature and extent. The report is organized as follows: • Section D.1 Introduction – presents the report objective and organization • Section D.2 Groundwater Evaluation Approach – provides a summary of the methods used for the evaluation • Section D.3 Field Work – provides a summary of field work performed to fill data gaps identified as part of this evaluation • Section D.4 Source Zone Evaluation – identifies chemicals of concern (COCs) in groundwater sourced from the RFI site • Section D.5 Nature and Extent – presents an assessment of the nature and extent of chemical impacts to groundwater beneath the RFI site • Section D.6 Fate and Transport – discusses potential routes of migration of chemicals in groundwater beneath the RFI site and provides a summary of plume stability analysis • Section D.7 Recommendations – presents CMS recommendations based on the evaluation performed The groundwater source zone and plume characterization evaluation involved a comprehensive review and evaluation of groundwater data from wells interpreted to be impacted by sources at the EEL RFI site. D-1 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory D.2 DRAFT June 2015 Groundwater Evaluation Approach Site data and the three-dimensional groundwater flow model developed for Santa Susana Field Laboratory as presented in the 2009 Draft Site-Wide Groundwater Remedial Investigation Report (MWH, 2009) were used to help evaluate groundwater flow directions at the EEL RFI site. The flow model was used to create forward and backward particle tracks (i.e., flow paths). The forward particle tracks depict how groundwater moves from source areas through the flow field. Chemical use area (CUA) cluster (CC) -specific forward particle tracks were developed for this evaluation to evaluate flow paths from the CC at the EEL RFI site. The backward particle tracks depict how groundwater moves through the flow field from a location (e.g., well) to its area of capture. Forward and backward particle tracking for both non-pumping and pumping conditions were reviewed, where the pumping condition represents a period of groundwater extraction at SSFL between 1995 and 1998. The forward particle tracking generated by the flow model represent groundwater flow paths at depths of either 10 or 200 meters below the water table. Particle releases at the water table to depths of 10 meters (33 feet) below the water table are used to represent chemicals released as solutes. Particle releases to depths of 200 meters (656 feet) below the water table are used to represent the transport of potential releases of dense non-aqueous phase solvents (DNAPL) such as trichloroethene (TCE). The 0to 10-meter flow paths are used to help interpret flow directions if there were no known DNAPL releases at a CC. The 0- to 200-meter flow paths are used if there was a known historical DNAPL release at a CC. The 0- to 10-meter particle tracks were used for EEL CC 1 because there is no indication in historical records or apparent in the characterization data that indicates DNAPL releases within the CC. The backward particle tracks illustrate the entire flow path and direction from the recharge area to the well location at depth locations across the open or screened interval of the well. The particle tracks were generated to a flowpath length of 1,000 meters as site data and contaminant transport simulations show this to be a reasonable upper bound estimate of plume extent. To estimate the extent of chemical transport from likely or confirmed sources at an RFI site, the length of forward particles paths (i.e., paths starting at sources and advancing through the flow field) were truncated based on the mean Darcy flux under both pumping and non-pumping conditions. The Darcy flux along the particle paths generated for an RFI site is equal to the total particle track length divided by the time it takes to flow along the flowpath based on a porosity of 1. The average of the computed Darcy flux values for particle paths under non-pumping and pumping conditions for the EEL RFI site was 4.63x10-10 meters per second (m/s) and 4.28x10-10 m/s, respectively. Results from contaminant transport simulations for D-2 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 three RFI sites at SSFL [as presented in the Draft Site-Wide Groundwater RI Report (MWH, 2009)] were used to create a plot of transport distance versus mean Darcy flux. A plot for the non-pumping and pumping conditions is shown in Attachment D-1. The mean Darcy flux for each RFI Site was then plotted on these figures and the estimated transport distance was taken from where the point intersects the horizontal axis. Forward particle paths for the EEL RFI site were truncated to 135 and 130 meters for the non-pumping and pumping conditions, respectively, as shown in Figure D-1. These estimated transport distances represent an upper bound estimate of the extent of contaminant distribution to site characterization levels at a time 50 years after a release. Wells interpreted to intercept groundwater flow from EEL were identified based on review of these truncated particle tracks. Available groundwater sampling results for wells interpreted to monitor the EEL RFI site were evaluated for the period of record through 2014. These data were screened against groundwater comparison values (GCLs) to evaluate the presence of chemicals at concentrations above their GCLs at the site and to identify data gaps. Groundwater comparison values (GCVs) used in the Potential Transport of Contaminants in Vadose Zone to Groundwater (Appendix C of this report), are numerically equivalent to GCLs. GCVs are presented in the Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (MWH, 2013; Appendix D of the DQO Report [CH2M HILL, 2013]) with applicable updates to regulatory screening levels if the updated levels are lower than those presented in Appendix D of the DQO Report. Additional screening levels were developed and documented in Final Development of Risk Based Screening Levels for Additional Groundwater Constituents and Screening Level Clarifications (MWH, 2014b) and Draft Development of Risk Based Screening Levels for Additional Groundwater Constituents Detected at the Santa Susana Field Laboratory (MWH, 2014d). Additional sampling was recommended if data gaps were identified based on review of historical data. A sensitivity analysis was performed on recent groundwater data (from 2010 to 2014) to identify results reported as not detected where the detection limit exceeds the established GCL. Additional sampling was recommended if data gaps were identified based on the sensitivity analysis. The methodology and steps involved in the sensitivity analysis are summarized in Figure D-2. A source zone evaluation was performed to identify COCs in groundwater sourced from the EEL RFI site. Assessment of the nature and extent of chemical impacts to groundwater beneath the EEL RFI site was performed by evaluating recent (2010 to 2014, with preliminary first quarter 2015 data at select wells) and historical groundwater data. The fate and transport of chemicals in groundwater at EEL was D-3 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 evaluated using plume stability analysis involving chemical trend analysis (Figure D-3), vapor intrusion evaluation (CH2M HILL, 2015), and evaluation of natural attenuation processes. Statistical trend analysis was performed to evaluate trends in concentration over time for chemicals identified as sources in the vadose zone at the EEL RFI site and chemicals detected in groundwater above GCLs in recent data (2010 to 2014) for wells in the vicinity of EEL. Groundwater data for these chemicals collected between 1984 and 2014 from wells selected for evaluation of the EEL RFI site were used for the trend analysis If TCE was included in the list of chemicals, TCE daughter products (1,1dichloroethene (DCE), cis-1,2-DCE, trans-1,2-DCE, and vinyl chloride) were also evaluated in the trend analysis. Trend analysis was performed for chemicals at well locations where greater than three sample results were available, and greater than 25 percent of total sample results had detections. The trend analysis was performed using the MannKendall test at a 99 percent confidence level using the commercially-available ProUCL software package. Non-detect results considered in the trend analysis were replaced with half of the quantitation limit. This method for trend analysis is consistent with the alternatives identified in the DQO Report (CH2MHILL, 2013). The methodology used for the trend analysis is summarized in a flowchart provided as Figure D-3. D.3 Field Work This section presents a summary of the field work performed in response to the data gaps that were identified during the groundwater evaluation. The following sampling recommendations (location – analyses) were made to supplement the groundwater sampling that was already recommended as part of the Potential Transport of Contaminants in Vadose Zone to Groundwater evaluation (Appendix C of this report) for EEL:  PZ-050 – sample for volatile organic compounds (VOCs), semi-volatile organic compounds (SVOCs), total petroleum hydrocarbons (TPH), and metals  PZ-051 – sample for VOCs  RS-37 – (installed in December 2013 (Appendix C)) sample for VOCs to provide updated VOC groundwater data for the southwestern portion of the site. No additional sampling recommendations were made based on the groundwater sensitivity analysis. Sampling was conducted during the first quarter of 2013 at well PZ-051. Sampling was attempted during the third quarter of 2013 and first quarter of 2014 at PZ-050 but the well could not be sampled due to D-4 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 insufficient water. Samples were collected at PZ-050 during the third quarter of 2014, but sampling procedures were modified since there was insufficient water to sample using low flow methods. A bailer was used to dewater the well and samples were collected by bailing water that recharged into the well. Sampling was conducted during October 2014 at well RS-37. Groundwater level monitoring, sampling, and analysis were conducted in accordance with the Field Sampling Plan and Quality Assurance Project Plan for groundwater (Appendices of the Regulated Unit and Site-Wide Program Water Quality Sampling and Analysis Plans (H&A, 2010a; 2010b)). Results are reported in the quarterly and/or annual groundwater monitoring and sampling reports (MWH 2014a, 2014c, 2014e, 2015). D.4 Source Zone Evaluation The source zone evaluation was performed to identify COCs in groundwater sourced from the RFI site. Source and chemical identification in surficial media as potential contaminant sources to groundwater at EEL are summarized in Tables 3-1, 3-2, and 4-1 in the main body of this report. The data available at EEL to evaluate sources includes soil matrix, soil vapor, and groundwater chemical sampling results. The following 11 chemical groups with chemicals detected above their respective screening values in the vadose zone at EEL were evaluated for potential releases to groundwater within and down-gradient of the RFI site: • VOCs • SVOCs • polycyclic aromatic hydrocarbons (PAHs) • energetics - perchlorate • TPHs • polychlorinated biphenyls (PCBs) • herbicides • pesticides • dioxins/furans • metals • inorganics D-5 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 Based on review of the particle tracks as described in Section D.2, wells selected for evaluating impacts to groundwater from chemicals in the vadose zone at EEL included: ES-23, ES-28, ES-29, ES-30, PZ038, PZ-039, PZ-050, RS-15, RS-17, and RS-37 because they are interpreted to monitor EEL (intercept flow paths from the RFI site) and contain groundwater representative of the EEL (not interpreted to be primarily impacted by an adjacent RFI site). Of the selected wells, three wells are located within the EEL RFI Site CC 1 boundary, with the remaining wells within adjacent RFI sites or along flow paths downgradient of the CCs. However, these wells are potentially impacted by adjacent RFI sites because of changes in flow direction from historical groundwater pumping. Adjacent RFI sites that have potential impacts to groundwater beneath EEL include Compound A Facility and Area III Sewage Treatment Plant (STP-III) to the east and Systems Test Laboratory IV (STL-IV) to the south. As such, it is difficult to definitively assign well locations to specific sources at the EEL RFI site given the long and varied history of groundwater withdrawals at SSFL that have altered flow directions over time. Recent (2010 to 2014, with preliminary first quarter 2015 data at select wells) and historical (prior to 2010) groundwater sampling results from these wells are summarized in Table D-1 and described in Table 4-4 in the main body of this report. Of the chemical groups identified and listed above as potential sources in the vadose zone, VOCs, TPHs and metals were detected in groundwater at concentrations above GCLs in recent data. No additional chemical groups had chemicals that were detected above GCLs in recent or historical data. Other chemicals outside of the chemicals identified as potential sources in the vadose zone that were detected in groundwater beneath or along flow paths from the EEL RFI at concentrations above GCLs in recent data included metals (chromium, copper, lithium, molybdenum, nickel, selenium, thallium and vanadium). These metals are near GCLs, are not interpreted to be sourced from EEL based on the available vadose zone data, and are interpreted to be representative of background concentrations. These results and the maximum detected concentrations are presented in Table D-1. D.5 Nature and Extent This section describes the assessment of the nature and extent of chemical impacts to groundwater beneath the EEL RFI site. Table D-1 provides a summary of recent (2010 to 2014 with preliminary first quarter 2015 data at select wells) and historical (prior to 2010) groundwater results, including number of locations (i.e. wells, seeps) sampled/analyzed, number of results, and maximum result, for chemicals either identified as sources in the vadose zone or detected in groundwater above GCLs for wells D-6 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 interpreted to monitor and contain groundwater representative of the EEL RFI Site. Table D-2 provides a summary of recent (2010 to 2014 with preliminary first quarter 2015 data at select wells) and historical (prior to 2010) groundwater results by well for chemicals identified as sources in the vadose and detected in groundwater above GCLs (exceeds screening levels in both the vadose zone and in groundwater). Table 4-4 in the main body of this report summarizes the nature and extent of these chemicals at EEL. VOCs represent the greatest groundwater impacts at the EEL RFI Site because they are found at the greatest extent and highest concentration relative to their GCLs of chemicals that are sourced from EEL. Figure D-1 shows well locations where VOCs are present above their GCLs. TPHs and metals were also detected in groundwater at concentrations above GCLs in recent data but the impacts to groundwater are within the lateral and vertical extents of the VOC impacts. VOCs detected in groundwater at concentrations above GCLs in recent data (2010 to 2014) that are sourced from EEL include cis-1,2-DCE and TCE. • cis-1,2-DCE was detected above its GCL at one well, RS-15, in 2 out of 2 results. Cis-1,2-DCE is recommended for CMS assessment in groundwater. • TCE was detected above its GCL at three wells: at ES-29 in three out of seven results, at ES-30 in one out of one result, and at RS-15 in two out of two results. TCE is recommended for CMS assessment in groundwater. Wells outside of those listed in Section D.4 above to evaluate groundwater impacts at the EEL RFI site were considered for evaluating the extent of the groundwater impacts sourced from EEL. The existing monitoring well network defines the extent of groundwater impacts described above. Although there are no vertically discrete sampling locations within EEL a combination of shallow and deeper wells within the monitoring network and further down-gradient defines the extent of the VOC impacts vertically. Sampling results from the vertical clusters to the west and southwest near STL-IV (RD-55A and B and RD-58A, B and C) and to the south of the Burro Flats fault (SP-882G) show that VOCs have been characterized to below or near GCLs. The lateral extent of TCE and cis-1,2-DCE plumes sourced from EEL are bounded by wells with concentrations less than the GCLs including RS-17 and RS-37 to the southwest and PZ-028 and PZ-051 to the northeast. Wells to the south and southwest are impacted by adjacent RFI sites including Compound A to the east and southeast, and STL-IV to the south. Threedimensional plume evaluations have been developed for groundwater impacts at the Subarea 5/9 south RFI sites. Descriptions and results are presented in Appendix B of the Subarea 5/9 South Data Summary and Findings Report. D-7 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 TPHs detected in groundwater at concentrations above GCLs in recent data (2010 to 2014) that are sourced from EEL include diesel range organics (DRO) with carbons ranges of C21-C30. • DRO (C21-C30) was detected above its GCL at two wells, at ES-30 in one out of two results and at PZ-050 at one out of one result. DRO is not recommended for CMS assessment. Diesel range organic concentrations in groundwater above GCLs are within the extent of the VOC impacts and extend from PZ-050 to the northwest but are bounded by wells with concentrations less than the GCL including RS-37 to the southwest, ES-26 to the south, and WS-11 to the east. Impacts to groundwater to the northeast are interpreted to be related to nearby RFI site Compound A. The elevated detections of DRO at wells ES-30 and PZ-050 are limited to one event at each well, and the elevated DRO at PZ-050 occurred during the sampling event where deviations from the standard, approved sampling procedures occurred due to an insufficient water column within the screened interval. Consequently, DRO is not recommended for CMS in groundwater; however, continued monitoring of the groundwater for DRO at EEL wells is recommended. Metals detected in groundwater at concentrations above GCLs in recent data (2010 to 2014) that were also detected above vadose zone screening levels in soil samples at EEL include cadmium and manganese. • Total cadmium and dissolved cadmium was detected above its GCL at one well, at PZ-050 in one out of one result. This result is from the sampling event where standard sampling procedures were not followed due to insufficient water in the well. Other wells sampled included ES-30 and RS-37 and cadmium (total and dissolved) was not detected. Cadmium is not recommended for CMS assessment. • Total manganese was detected above its GCL at one well, at PZ-050 in one out of one result (dissolved manganese was detected at PZ-050 but was well below the GCL). This result above the GCL is from the sampling event where standard sampling procedures were not followed due to insufficient water in the well. Other wells sampled included RS-37 and manganese (total and dissolved) was detected below the GCL. Manganese is not recommended for CMS assessment. Sampling conducted to date shows the cadmium and manganese exceeding GCLs in groundwater at EEL to be localized to an individual well and results have not been confirmed by verification sampling. Data is not adequate to recommend either chemical for CMS assessment; however, further groundwater monitoring to confirm the single elevated detections at PZ-050 is recommended. D-8 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory D.6 DRAFT June 2015 Fate and Transport The fate and transport of chemicals in groundwater was evaluated using plume stability analysis, vapor intrusion evaluation, and evaluation of natural attenuation processes as described below. The potential transport of chemicals of concern at the EEL RFI Site was assessed by plume stability analysis. Statistical trend analysis was performed to evaluate trends in concentration over time for chemicals identified as sources in the vadose zone at the EEL RFI Site and chemicals detected in groundwater above GCLs in recent data (2010 to 2014) for wells in the vicinity of the EEL RFI Site. Trend analysis results for TCE are displayed on Figure D-1. Trend analysis results are summarized in Table D-3 and trend graphs are presented by well and chemical in Attachment D-2. No increasing chemical trends were identified in the trend analysis for the EEL RFI Site. All trends were decreasing or indeterminate. The following decreasing trends were identified: • 1,1-DCE –at ES-23 and ES-30 • TCE –at ES-23, ES-28 and RS-15 No concentration trend was identified for DRO (i.e., result of trend analysis was indeterminate); however the extent of the plume is within the known extent of the TCE plume which has stable lateral boundaries defined within the monitoring network. No trends were identified for cadmium or because sufficient data was not available to determine a trend. Groundwater data at the EEL RFI Site was evaluated for vapor intrusion in the Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South Technical Memo (CH2MHILL, 2015). Evaluation of natural attenuation processes at SSFL was performed in the Site Conceptual Model in the Draft Site-Wide Groundwater Remedial Investigation Report (MWH, 2009) and will be further evaluated in results from treatability studies currently underway or being planned, and in the corrective measures study report. Further evaluations of contaminant transport and fate may be conducted as outlined by the Department of Toxic Substances Control (2014). D.7 Recommendations Findings of the groundwater evaluation for the EEL RFI Site indicate five chemicals sourced from EEL are present in groundwater above GCLs: cis-1,2-DCE, TCE, DRO, manganese, and cadmium. D-9 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 Based on evaluation of the source zone, nature and extent, and fate and transport of chemicals in groundwater at the EEL RFI Site, the following chemicals are recommended for CMS assessment in groundwater: • cis-1,2-DCE • TCE The footprint of impacted groundwater for the EEL RFI Site is depicted in Figure 4-7 of the main body of this report. The following chemicals are recommended for further monitoring at the specified wells because data was not sufficient to make recommendations for CMS or no further action (NFA): • cadmium – at PZ-050 • manganese – at PZ-050 • DRO – at PZ-050 and ES-30 D-10 Appendix D: Groundwater Source Zone and Plume Characterization Environmental Effects Laboratory DRAFT June 2015 REFERENCES CH2M HILL, 2013. Comprehensive Data Quality Objectives, RCRA Field Investigation Santa Susana Field Laboratory, Ventura County, CA. March. CH2M HILL, 2015. Vapor Intrusion Assessment, Boeing RFI Subarea 5/9 South Technical Memorandum, Santa Susana Field Laboratory, Ventura County, CA. February. Department of Toxic Substances Control, 2014. Letter from Mark Malinowski to David Dassler, John Jones, and Allen Elliott, Reporting of Characterization Work for the Chatsworth Formation Operable Unit at the Santa Susana Field Laboratory, Ventura County, California. September 30. Haley & Aldrich, Inc. (H&A), 2010a. Regulated Unit Water Quality Sampling and Analysis Plan, Areas I and III, Post-Closure Permit PC-94/95-3-02, Santa Susana Field Laboratory, Ventura County, California. April. H&A, 2010b. Site-Wide Water Quality Sampling and Analysis Plan, Revision 1, Santa Susana Field Laboratory, Ventura County, California. December. MWH, 2009. Draft Site-Wide Groundwater Remedial Investigation Report, Santa Susana Field Laboratory, Ventura County, California. Volumes 1 through 7. In Association with the SSFL Groundwater Advisory Panel, University of Guelph, Haley & Aldrich and AquaResource Inc. December. MWH, 2013. Recommended Approach for Evaluating Vadose Zone Mass Flux of Contaminants to Groundwater (Appendix D of Comprehensive Data Quality Objectives, CH2M HILL, 2013). March 5. MWH, 2014a. Report on Annual Groundwater Monitoring, 2014, Santa Susana Field Laboratory, Ventura County, CA. January 3. MWH, 2014b. Final Development of Risk Based Screening Levels for Additional Groundwater Constituents, and Screening Level Clarifications at the Santa Susana Field Laboratory, Santa Susana, California. May 16. MWH, 2014c. Groundwater Monitoring Progress Report, First Quarter 2014, Revision 1, Santa Susana Field Laboratory, Ventura County, CA. June 16. MWH, 2014d. Draft Development of Risk Based Screening Levels for Additional Groundwater Constituents Detected at the Santa Susana Field Laboratory, Santa Susana, CA. November 11. MWH, 2014e. Groundwater Monitoring Progress Report, Third Quarter 2014, Santa Susana Field Laboratory, Ventura County, CA. November 21. MWH, 2015. Report on Annual Groundwater Monitoring, 2014, Santa Susana Field Laboratory, Ventura County, California. February 20. D-11 FIGURES TCE Trend Decreasing ! ( ! ( ! ( Stable Indeterminate Aerial Photo circa 1967 ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! STP-3 ! ! ! ! ! g ( ! g E ( ! g PZ-054 g PZ-149 PZ-053 ( ! E ( ! E ( ! ! ( ( RS-17 ! PZ-038 ! ( Compound A HAR-17 STL-IV !! ( E ( RD-58A E ( E ! ES-28 g PZ-037 RD-58C PZ-050 ! ( PZ-039 ES-32 HAR-18 ! ( E ! ! ( E ! HAR-34 ! RD-55A ! RS-15 ( ( ( ES-30 (! ! (! ! ES-23 ES-29 EEL RS-37 RS-09 ( E ! ( PZ-051 ! ! g PZ-036 ! ( ( ! E RS-12 ES-24 ( ! E PZ-034 ( ! E ( E! ( ! ES-15 Compound A ES-16 HAR-32 ( ! ES-14 ES-25 ! ( HAR-33 E RS-33 ( ! ! ( E ( E ! EE ( ! ! ( ES-26 ! ( E ! ( E ( E ! RS-14 ( E ! ( E ! ( E ( PZ-015A-G ! E ! ES-17 PZ-039 RD-55B g (/ ! ( E ! ! STP-3 WS-11 ! ! ( ! ES-28 PZ-038 ! PZ-028 ! ( E PZ-029 ( ! EEL ES-29 ! ( ! ( ( PZ-030 ! (/ ! ! /( ( ! ES-30 PZ-050 ! ( ( PZ-031 ! ! ( ( RS-17 ! ! ! PZ-018A-E RS-15 RS-37 ! ES-23 ! ( ! PZ-051 HAR-28 HAR-27 PZ-040 STL-IV HAR-29 (! ( !! ( E ( ! HAR-07 RD-58B ! RS-13 ! ! ! ! ( E ( WS-09A E ! g g Basemap E ( ! RD-67 ! TCE Exceedance = ! E ( ( ! ! ( ! Wells impacted from sources other than EEL ( ! SP-882A-D,G ! Faults Deformation Bands Structures Finer Grained Unit (shale/siltstone) g g Area in Which Finer Grained Unit May Be Discontinuous g Exceedance likely associated with EEL Exceedance likely associated with EEL and/or adjacent site No exceedance g Administrative Boundaries Transport-truncated Flow Paths ! ! RFI Group Boundary Boeing RFI Site Boundary 95-98 Groundwater Pumping Condition 0-10 meters Non-pumping Condition 0-10 meters E ( ! RD-06 DOE RFI Site Boundary CUA Clusters Panel 1 Assessment of Contaminant Distribution To evaluate the distribution and extent of EEL contaminants in g roundwater, existing site data were evaluated in combination with results from groundwater flow and contaminant transport simulations (as presented in the Draft SSFL Site -Wide Groundwater RI Report, MWH 2009). This information assists in confirming the effectiveness of the monitoring network and the extent of contaminant impacts. Blue lines show forward particle flow paths from CC-1 at the EEL site to a depth of 10 meters below the water table under a non -pumping condition. Black lines represent flow paths from CC-1 to a depth of 10 meters below the water table during a historical period of groundwater extraction at SSFL between 1995 and 1998. The lengths of the flow paths are truncated to 443 and 427 feet for the non -pumping and pumping conditions, respectively. These estimated transport distances represent an upper bound estimate of the extent of contaminant distribution to site characterization levels. TCE wa s selected to represent the extent of impacts since it is found at the greatest extent and highest concentration relative to its comparison value. Wells colored in red contain or have historically contained concentrations of TCE above groundwater characterization levels, while those colored in green hav e never had concentrations exceed groundwater characterization levels. Please Note: The original version of this figure includes colorized features and shading. A black and white copy of the figure should not be used because it may not accurately represent the information presented. Note: non-detect values are shown on these graphs as detects because 1/2 of the detection limit was used for the trend analysis. ± 0 580 1 inch = 580 feet Panel 2 Assessment of Plume Stability To evaluate if the lateral or vertical extent of contaminated groundwater is increasing, a statistical trend evaluation (99% confidence level) was conducted for chemical concentration data from wells associated with EEL RFI site over the full period of record through December 31, 2014 for all chemicals that have GCLs established. This panel shows the results of the statistical evaluation for TCE. Statistically significant decreasing TCE concentration trends (wells shown in green) were found in 2 of the 6 wells, no trend (stable) was measured in 3 wells, and one well (PZ-050) did not have enough data available to determine a trend. Concentration trend graphs for a well (RS-15) near the source and a clean well beyond the plume (RS-17) are provided on the right. No well showed a statistically significant increasing TCE trend. Additionally, 2014 results at well RS-37, installed in 2013 as a replacement for RS-17, showed TCE concentrations below its groundwater characterization level. This assessment shows that the lateral boundary of the plume as defined by the monitoring network is stable. DRAFT SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA SUMMARY EVALUATION OF GROUNDWATER ASSESSMENT AT EEL Figure D-1 Path: U:\BoeingSantaSusana\MXD\Vadose Zone Mass Flux\EEL.mxd 1,160 Feet Obtain 2010current GW data for the wells at the RFI site in question. Use the countifs excel function to determine the 1) number of results, 2) number of detects, 3) number of NDs and 4) number of NDs>GCV, per chemical, per well Formulate a list of wells and chemicals that have elevated NDs at the RFI site. Filter the GW data for elevated NDs (i.e. NDs that exceed the GCV) No Calculate the %NDs that exceed the GCV for each chemical at each well location. ((NDs>GCV)/ (Total NDs))*100 Calculate the %Detects for each chemical at each well location. ((# of Detects)/(Total number of results))*100 Is the % NDs > 50% and the % detects < 25% for a given chemical at one well location? Yes No Additional Sampling is Recommended No Is the chemical a COC at the RFI site? Yes Is the chemical already recommended for sampling in the VZ to GW evaluation or the GWRI data gap sampling or is it routinely monitored under the monitoring program? Yes Yes Does the analytical method currently being used have a MDL below the GCV? No No Recommend Additional Sampling Does the analytical method currently being used have a MDL below the GCV? Yes No Is there another analytical method or low level prep that can be used to achieve a MDL lower than the screening value? No Yes Recommend sampling and analysis with alternate analytical method Abbreviations: COC – chemical of concern GCV – groundwater comparison value GW – groundwater MDL – method detection limit ND – not-detected VZ – vadose zone SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA GROUNDWATER SENSITIVITY ANALYSIS APPROACH FIGURE D-2 Step 1 – Obtain List of Wells and COCs Obtain list of wells1 and site-associated chemicals2, 3 at the RFI Site Step 2 – Groundwater Data Evaluation Obtain unique4 site-associated chemical groundwater data5 collected from 19846 to 2014 at the wells selected during evaluation at the RFI Site. Chemical detected in > 25% of the total sample results?5 Yes More than three unique4 sample results available? No Yes No Step 3 – Statistical Trend Analysis Abbreviations BTVs – background threshold value COC – chemical of concern DCE – dichloroethene GCVs – groundwater comparison values RFI – RCRA Facility Investigation SSFL – Santa Susana Field Laboratory TCE – trichloroethene Trend analysis was not performed Notes 1. List of wells – wells selected for evaluation in Appendix C and D (see Table C-1 and Table D-1 for the list of wells). 2. List of site-associate chemicals – combine list of (1) chemicals detected above BTVs or GCVs in the vadose zone samples (see Vadose Zone Data Evaluation in Table C-1 of Appendix C); and (2) chemicals detected above GCVs in 2010-2014 groundwater samples (see Groundwater Data Evaluation in Table D-1 of Appendix D). 3. If TCE is included as a site-associated chemical, TCE daughter products (1,1-DCE. cis-1,2-DCE, trans-1,2-DCE, and vinyl chloride) will also be evaluated. TCE daughter products are biodegraded products resulting from natural dehalohydrolysis of TCE in the environment. 4. Unique – if multiple samples collected on same date, use maximum result in the trend analysis 5. Non-detect results considered in the trend analysis are replaced with ½ of the quantitation limit. 6. 1984 indicates the year groundwater characterization began at SSFL. Perform 99% confidence level Mann-Kendall trend analysis SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA STATISTICAL TREND ANALYSIS EVALUATION METHODOLOGY FIGURE D-3 TABLES TABLE D-1 SUMMARY OF GROUNDWATER RESULTS FOR EEL EEL RFI SITE, BOEING SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY CA Chemical Group VOCs Chemical Exceeds in GW Identified as Potential Source in Vadose Historical 2010 (prior to Zone 2014 2010) PAH PAH PAH PAH PAH PAH PAH PAH PAH PAH 1,1-Dichloroethene Benzene cis-1,2-Dichloroethene Trichloroethene bis(2-Ethylhexyl) phthalate Di-n-octyl phthalate Benzo(a)pyrene TEQ (a) Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3-cd)pyrene 2-Methylnaphthalene Acenaphthene Acenaphthylene Anthracene X X X X X X X X X X X PAH PAH PAH PAH PAH PAH Energetics Benzo(ghi)perylene (1) Fluoranthene Fluorene Naphthalene Phenanthrene Pyrene Perchlorate X X X X X X X TPH (b) TPH Diesel Range Organics (C15-C20) Diesel Range Organics (C21-C30) Diesel Range Organics (C8-C30) Oil Range Organics (C30-C40) Aroclor 1254 Aroclor 1260 2,4-Dichlorophenoxybutyric acid MCPA Silvex 4,4'-DDD 4,4'-DDT beta-BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex X X VOCs VOCs SVOCs SVOCs PAH TPH PCB PCB Herbicides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides See last page for notes and abbreviations. X X X X X X X X X X X X X X X X X X X X X X X X X X X GCL Units 6 ug/L 1 ug/L 6 ug/L 5 ug/L 4 ug/L 500 ug/L 0 ug/L 0 ug/L 0.2 ug/L 0 ug/L 0 ug/L 0 ug/L 0 ug/L 0 ug/L 50 ug/L 380 ug/L 380 ug/L 3800 ug/L N/A 250 ug/L 250 ug/L 17 ug/L 3800 ug/L 380 ug/L 6 ug/L 0.1 0.1 0.1 0.74 0.5 0.5 100 6.3 50 0.62 0.44 0.025 75 75 2 3.8 0.01 0.01 0.0082 mg/L mg/L mg/L mg/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L Groundwater Results for Wells that Monitor and Contain Groundwater Representative of EEL ES-23, ES-28, ES-29, ES-30, PZ-038, PZ-039, PZ-050, RS-15, RS-17, RS-37 Historical Data (prior to 2010) Recent Data (2010 - 2014) No. of No. of Locations No. of Locations with Locations Sampled/A Detections No. of No. Maximu Exceedanc No. of Detected Number of No. Maximum nalyzed >GCL Results Detects m Result e Factor Locations >GCL Results Detects Result 9 3 125 44 23 3.8 5 0 12 8 0.37 9 1 103 1 6 6.0 4 0 12 0 ND 9 2 90 31 31 5.2 5 1 12 5 13 9 7 125 116 1400 280.0 5 3 12 11 87 3 0 5 0 ND N/A 4 0 6 2 0.4 3 0 5 0 ND N/A 4 0 6 0 ND 0 0 0 4 10 0 3 5 0 4 6 0 3 5 0 4 6 0 3 5 0 4 6 0 ND ND N/A 0 ND 3 5 0 4 6 0 3 5 0 4 6 0 3 5 0 4 6 0 3 5 0 4 6 0 0 0 0 0 N/A N/A 4 0 6 0 ND 3 0 5 0 ND N/A 4 0 6 0 ND 3 0 5 0 ND N/A 4 0 6 0 ND 3 0 5 0 ND N/A 4 0 6 0 ND Exceedance Factor 0.1 N/A 2.2 17.4 0.1 N/A N/A N/A N/A N/A N/A 3 3 3 3 3 2 7 0 0 0 0 0 0 0 0 5 5 5 5 2 10 0 0 0 0 0 0 1 ND ND ND ND ND ND 0.796 N/A N/A N/A N/A N/A N/A 0.1 4 4 4 4 4 4 1 0 0 0 0 0 0 0 0 6 6 6 6 6 1 0 1 0 1 0 1 1 ND 0.0083 ND 0.008 ND 0.024 0.83 N/A 0.00003 N/A 0.0005 N/A 0.0001 0.1 1 1 1 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 3 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ND ND ND ND N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 3 3 3 3 3 3 2 2 2 3 3 3 3 3 3 3 3 3 3 0 2 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 5 5 3 3 3 2 2 2 3 3 3 3 3 3 3 3 3 3 0 2 2 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ND 0.81 0.88 0.39 ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND N/A 8.1 8.8 0.5 N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A Page 1 of 3 DRAFT TABLE D-1 SUMMARY OF GROUNDWATER RESULTS FOR EEL EEL RFI SITE, BOEING SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY CA Chemical Group Chemical (c) Dioxins/Furans 2,3,7,8-TCDD TEQ 1,2,3,4,6,7,8-Heptachlorodibenzofuran Dioxins/Furans 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin Dioxins/Furans 1,2,3,4,7,8,9-Heptachlorodibenzofuran Dioxins/Furans 1,2,3,4,7,8-Hexachlorodibenzofuran Dioxins/Furans 1,2,3,4,7,8-Hexachlorodibenzo-p-dioxin Dioxins/Furans 1,2,3,6,7,8-Hexachlorodibenzofuran Dioxins/Furans 1,2,3,6,7,8-Hexachlorodibenzo-p-dioxin Dioxins/Furans 1,2,3,7,8,9-Hexachlorodibenzofuran Dioxins/Furans 1,2,3,7,8,9-Hexachlorodibenzo-p-dioxin Dioxins/Furans 1,2,3,7,8-Pentachlorodibenzofuran Dioxins/Furans 1,2,3,7,8-Pentachlorodibenzo-p-dioxin Dioxins/Furans 2,3,4,6,7,8-Hexachlorodibenzofuran Dioxins/Furans 2,3,4,7,8-Pentachlorodibenzofuran Dioxins/Furans 2,3,7,8-TCDD Dioxins/Furans 2,3,7,8-Tetrachlorodibenzofuran Dioxins/Furans Octachlorodibenzofuran Dioxins/Furans Octachlorodibenzo-p-dioxin Metals Antimony Metals Antimony, Dissolved Metals Arsenic Metals Arsenic, Dissolved Metals Barium Metals Barium, Dissolved Metals Beryllium Metals Beryllium, Dissolved Metals Boron Metals Boron, Dissolved Metals Cadmium Metals Cadmium, Dissolved Metals Chromium Metals Chromium, Dissolved Metals Copper Metals Copper, Dissolved Metals Hexavalent Chromium Metals Lithium Metals Lithium, Dissolved Metals Manganese Metals Manganese, Dissolved Metals Mercury Metals Mercury, Dissolved Metals Molybdenum Metals Molybdenum, Dissolved Metals Nickel Metals Nickel, Dissolved See last page for notes and abbreviations. Exceeds in GW Identified as Potential Source in Vadose Historical 2010 (prior to Zone 2014 2010) GCL 30 X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Groundwater Results for Wells that Monitor and Contain Groundwater Representative of EEL ES-23, ES-28, ES-29, ES-30, PZ-038, PZ-039, PZ-050, RS-15, RS-17, RS-37 Historical Data (prior to 2010) Recent Data (2010 - 2014) Units No. of No. of Locations No. of Locations with Locations Sampled/A Detections No. of No. Maximu Exceedanc No. of Detected Number of No. Maximum nalyzed >GCL Results Detects m Result e Factor Locations >GCL Results Detects Result pg/L N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A N/A 0.0025 mg/L 0.0025 mg/L 0.0077 mg/L 0.0077 mg/L 0.15 mg/L 0.15 mg/L 0.00014 mg/L 0.00014 mg/L 0.34 mg/L 0.34 mg/L 0.0002 mg/L 0.0002 mg/L 0.014 mg/L 0.014 mg/L 0.0047 mg/L 0.0047 mg/L 0.01 mg/L 0.025 mg/L 0.025 mg/L 0.15 mg/L 0.15 mg/L 6.3E-05 mg/L 6.3E-05 mg/L 0.0022 mg/L 0.0022 mg/L 0.017 mg/L 0.017 mg/L 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 0 5 0 5 0 5 0 5 0 5 0 5 0 5 0 0 0 0 3 0 5 0 5 0 5 N/A 0 0 0 0 0 0 0 0 0 1 0 1 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 Page 2 of 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7 0 7 0 7 0 14 0 9 0 7 0 7 0 7 0 0 0 0 5 0 7 0 7 0 7 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 5 0 0 0 7 0 2 0 0 0 2 0 0 0 0 3 0 0 0 0 0 3 N/A N/A N/A ND N/A 0.0032 N/A 0.1 N/A ND N/A 0.48 N/A 0.00022 N/A ND N/A 0.0094 N/A N/A N/A N/A 0.0572 N/A ND N/A ND N/A 0.0015 N/A N/A N/A 0.4 N/A 0.7 N/A N/A N/A 1.4 N/A 1.1 N/A N/A N/A 2.0 N/A N/A N/A N/A 0.4 N/A N/A N/A N/A N/A 0.1 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 3 3 3 3 3 3 3 3 0 0 3 3 2 4 2 2 3 2 2 2 2 3 3 2 2 2 2 0 0 0 0 0 0 0 0 0 0 0 1 1 1 0 1 0 0 2 2 1 0 0 0 1 1 1 0 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 4 5 5 5 5 5 5 5 5 0 0 5 5 3 3 3 3 3 4 4 2 2 5 5 3 3 3 3 4 0 0 0 0 0 0 0 0 2 0 1 0 0 0 0 0 1 1 2 5 5 5 5 2 0 0 0 1 1 1 2 2 1 0 4 4 2 2 0 0 3 3 2 2 Exceedance Factor 0.1 0.0033 0.00085 0.0015 0.003 0.0012 0.14 0.084 0.00014 ND N/A N/A 0.0019 0.00086 0.1 0.00086 0.098 0.0025 ND 0.062 0.059 0.16 0.008 ND ND 0.0055 0.0027 0.087 0.013 0.3 0.6 0.4 0.2 0.9 0.6 1.0 N/A N/A N/A 9.5 4.3 7.1 0.1 20.9 0.5 N/A 2.5 2.4 1.1 0.1 N/A N/A 2.5 1.2 5.1 0.8 DRAFT TABLE D-1 SUMMARY OF GROUNDWATER RESULTS FOR EEL EEL RFI SITE, BOEING SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY CA Chemical Group Metals cont. Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Metals Inorganics Inorganics Inorganics Chemical Potassium Potassium, Dissolved Selenium Selenium, Dissolved Silver Silver, Dissolved Sodium Sodium, Dissolved Strontium Strontium, Dissolved Thallium Thallium, Dissolved Vanadium Vanadium, Dissolved Chloride Fluoride Nitrate-NO3 Exceeds in GW Identified as Potential Source in Vadose Historical 2010 (prior to Zone 2014 2010) X X X X X X X X X X X X X X GCL 9.6 9.6 0.0016 0.0016 0.00017 0.00017 190 190 0.8 0.8 0.00013 0.00013 0.0026 0.0026 250 0.8 45000 Units mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L mg/L ug/L Groundwater Results for Wells that Monitor and Contain Groundwater Representative of EEL ES-23, ES-28, ES-29, ES-30, PZ-038, PZ-039, PZ-050, RS-15, RS-17, RS-37 Historical Data (prior to 2010) Recent Data (2010 - 2014) No. of No. of Locations No. of Locations with Locations Sampled/A Detections No. of No. Maximu Exceedanc No. of Detected Number of No. Maximum nalyzed >GCL Results Detects m Result e Factor Locations >GCL Results Detects Result 0 0 0 0 N/A N/A 0 0 0 0 N/A 4 1 6 6 15 1.6 0 0 0 0 N/A 0 0 0 0 N/A N/A 2 1 3 1 0.0021 5 1 7 2 0.0077 4.8 2 1 3 1 0.0021 0 0 0 0 N/A N/A 3 0 6 2 0.000046 5 0 7 0 ND N/A 3 0 6 0 ND 0 0 0 0 N/A N/A 3 0 5 5 120 4 0 6 6 167 0.9 3 0 5 5 120 0 0 0 0 N/A N/A 0 0 0 0 N/A 3 1 5 5 0.829 1.0 0 0 0 0 N/A 0 0 0 0 N/A N/A 2 1 3 2 0.00014 5 0 7 0 ND N/A 2 0 3 0 ND 0 0 0 0 N/A N/A 2 1 3 6 0.0033 1 1 3 4 0.0042 1.6 2 0 3 6 0.0015 4 1 6 6 254 1.0 2 0 8 8 93 4 0 6 6 0.5 0.6 0 0 0 0 N/A 4 3 8 8 69600 1.5 3 0 10 10 23000 Exceedance Factor N/A N/A 1.3 1.3 0.3 N/A 0.6 0.6 N/A N/A 1.1 N/A 1.3 0.6 0.4 N/A 0.5 Notes/Abbreviations (a) - In groundwater, the seven generally recognized carcinogenic PAHs (Benzo(a)anthracene, Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Chrysene, Dibenzo(a,h)anthracene, and Indeno(1,2,3-cd)pyrene) are screened by comparing the calculated Benzo(a)pyrene TEQ values against the Benzo(a)pyrene screening value. (b) - In groundwater, TPH analyses falling under the typical GRO (C6-C12), DRO (C13-C30), and ORO (C30-C40) carbon ranges are evaluated together for comparison against vadose zone GRO, DRO, and ORO analyses, as the carbon ranges analyzed in the vadose zone and in groundwater do not match up in many cases. (c) - In groundwater, dioxins and furans are screened by comparing the calculated 2,3,7,8-TCDD TEQ values against the 2,3,7,8-TCDD screening value. (1) - There is no groundwater screening level established for benzo(ghi)perylene - this chemical is a potential human health concern, but no toxicity criterion is available for it. -EEL GCL N/A ND No. TEQ mg/L ug/L pg/L TCDD not evaluated Environmental Effects Laboratory groundwater characterization level not applicable not detected number toxic equivalence quotient milligrams per liter micrograms per liter picograms per liter tetrachlorodibenzo-p-dioxin See last page for notes and abbreviations. MCPA DDD DDT BHC Methylchlorophenoxypropionic Acid Dichlorodiphenyldichloroethane Dichlorodiphenyltrichloroethane Benzene hexachlorocyclohexane Page 3 of 3 DRAFT TABLE D-2 GROUNDWATER RESULTS FOR CHEMICALS SOURCED FROM VADOSE ZONE EEL RFI SITE, BOEING SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY CA Chemical cis-1,2-Dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene cis-1,2-dichloroethene Trichloroethene Trichloroethene Trichloroethene Trichloroethene Trichloroethene Trichloroethene Trichloroethene Trichloroethene Trichloroethene Diesel range organics (C21-C30) Diesel range organics (C21-C30) Diesel range organics (C21-C30) Cadmium Cadmium Cadmium Cadmium, Dissolved Cadmium, Dissolved Cadmium, Dissolved Cadmium, Dissolved Cadmium, Dissolved Cadmium, Dissolved Manganese Manganese Manganese, Dissolved Manganese, Dissolved Manganese, Dissolved See last page for notes and abbreviations. GCL 6 6 6 6 6 6 6 6 6 5 5 5 5 5 5 5 5 5 100 100 100 0.0002 0.2 0.2 0.0002 0.2 0.2 0.2 0.2 0.2 0.15 150 0.15 150 150 Units ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L ug/L mg/L ug/L ug/L mg/L ug/L ug/L ug/L ug/L ug/L mg/L ug/L mg/L ug/L ug/L Location ES-23 ES-28 ES-29 ES-30 PZ-038 PZ-039 PZ-050 RS-15 RS-37 ES-23 ES-28 ES-29 ES-30 PZ-038 PZ-039 PZ-050 RS-15 RS-37 ES-30 PZ-050 RS-37 ES-30 PZ-050 RS-37 ES-28 ES-29 ES-30 PZ-050 RS-15 RS-37 PZ-050 RS-37 PZ-050 RS-15 RS-37 Total No. of Results No. of Detected Results 34 3 2 35 2 1 2 7 -39 6 7 38 2 1 2 17 --3 ----1 1 -3 1 ---3 1 -- 15 0 0 15 1 0 0 0 -39 6 6 37 1 0 2 17 --0 ----0 0 -2 0 ---3 0 -- Historical Data (prior to 2010) No. of Results Detected above Result Date GCL 4 0 0 4 0 0 0 0 -39 6 6 37 1 0 1 17 --0 ----0 0 -1 0 ---0 0 -- <0.3 <0.2 <1 <0.2 2 <5 <5 <0.4 -19 16 <1 <1 <5 <5 1 130 --<0.099 ----<0.003 <0.003 -<0.000099 <0.005 ---0.029 <0.01 -- 2/7/1998 8/18/1998 3/4/1991 3/1/1996 6/2/2003 5/30/2001 5/14/2001 8/17/1998 -2/20/2003 2/4/1987 12/7/1988 2/6/1987 5/24/2001 5/30/2001 5/14/2001 8/17/1998 --2/10/2009 ----2/18/1999 2/18/1999 -2/19/2008 6/13/1985 ---5/7/2008 6/13/1985 -- Page 1 of 2 Result Date Total No. of Results 25 <4 <2 31 2 <5 <5 <10 -670 140 64 480 53 <5 8 1400 --<0.2 ----<3 <3 -0.22 <5 ---57.2 <10 -- 9/8/2008 3/8/1992 3/8/1992 8/30/2006 6/2/2003 5/30/2001 5/14/2001 12/10/1990 -3/7/1993 3/8/1992 3/8/1992 4/13/1987 6/2/2003 5/30/2001 6/3/2003 12/10/1986 --2/19/2008 ----2/18/1999 2/18/1999 -2/10/2009 6/13/1985 ---2/19/2008 6/13/1985 -- --7 1 ---2 1 --7 1 ---2 1 2 1 2 2 1 2 --2 1 -2 1 1 1 -1 No. of Detected Results --2 1 ---2 0 --7 1 ---2 1 1 1 0 0 1 0 --0 1 -0 1 1 1 -1 Recent Data (2010 - 2014) No. of Results Detected above Result Date GCL --0 0 ---2 0 --3 1 ---2 0 1 1 0 0 1 0 --0 1 -0 1 0 0 -0 --<0.15 0.9 ---9.5 <0.15 --2.8 41 ---60 0.94 <0.099 0.28 <0.094 <0.0001 0.0019 <0.0001 --<0.0001 0.00086 -<0.0001 0.16 0.0064 0.008 -0.0011 --7/22/2011 2/10/2010 ---1/17/2011 10/13/2014 --7/31/2012 2/10/2010 ---1/13/2011 10/13/2014 1/31/2014 4/28/2014 7/24/2014 7/22/2013 4/29/2014 2/10/2014 --7/22/2013 4/29/2014 -2/10/2014 4/29/2014 7/24/2014 4/29/2014 -7/24/2014 Result Date --0.3 0.9 ---13 <0.15 --19 41 ---87 0.94 0.81 0.28 <0.095 <0.1 1.9 <0.1 --<0.1 0.86 -<0.1 160 6.4 8 -1.1 --9/3/2010 2/10/2010 ---1/13/2011 10/13/2014 --1/24/2012 2/10/2010 ---1/17/2011 10/13/2014 7/22/2013 4/28/2014 2/10/2014 7/22/2013 4/29/2014 2/10/2014 --7/22/2013 4/29/2014 -2/10/2014 4/29/2014 7/24/2014 4/29/2014 -7/24/2014 DRAFT TABLE D-2 GROUNDWATER RESULTS FOR CHEMICALS SOURCED FROM VADOSE ZONE EEL RFI SITE, BOEING SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY CA Notes and Abbreviations 1 - If all results are not-detected, minimum and maximum results are reported as < quantitation limit GCL - Groundwater Characterization Level No. - Number µg/L - micrograms per liter mg/L - milligrams per liter See last page for notes and abbreviations. Page 2 of 2 DRAFT TABLE D-3 STATISTICAL TREND ANALYSIS RESULTS EEL RFI SITE, BOEING SUB-AREA 5/9 SOUTH DATA SUMMARY AND FINDINGS REPORT SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY CA EEL RFI Site Boeing Sub-Area 5/9 South ES-23 ES-28 ES-29 ES-30 PZ-050 RS-15 RS-17 1,1-dichloroethene cis-1,2-dichloroethene trichloroethene 1,1-dichloroethene trichloroethene 1,1-dichloroethene cis-1,2-dichloroethene nitrate-no3 trichloroethene 1,1-dichloroethene cis-1,2-dichloroethene trichloroethene bis(2-ethylhexyl) phthalate cadmium, dissolved diesel range organics (c21-c30) 1,1-dichloroethene cis-1,2-dichloroethene nitrate-no3 trichloroethene trichloroethene General Statistics Mann-Kendall Test Number or Number of Number Standard Trend at 99% Reported Geometric Standard Test Value Tabulated Standardized Approximate Generated Values Minimum Maximum Mean Median Deviation Confidence Events Not Mean Deviation (S) p-value Value of S p-value Events Reported (n) of S Level? Used 0 35 35 0.05 10 1.369 0.603 0.5 2.02 -217 -2.326 70.16 -3.079 0.00104 Decreasing 0 30 30 0.15 25 3.314 1.015 0.655 6.068 28 2.326 55.96 0.483 0.315 Indeterminate 0 35 35 19 670 189.6 122.7 120 177.1 -370 -2.326 70.36 -5.244 7.84E-08 Decreasing 0 6 6 0.5 4 1.7 1.333 1.5 1.296 0 0.5 5.228 N/A N/A Indeterminate 0 6 6 16 140 69.83 54.58 55.5 49.38 7 0.136 5.323 1.127 0.13 Indeterminate 0 12 12 0.115 8 1.889 0.714 0.415 2.656 -44 0.001 14.51 -2.963 0.00153 Decreasing 0 8 8 0.075 1 0.283 0.172 0.118 0.327 -12 0.089 7.528 -1.461 0.072 Indeterminate 0 7 7 20000 69600 27800 24724 21000 18463 -3 0.386 6.298 -0.318 0.375 Indeterminate 0 12 12 2.8 64 25.89 16.49 26 21.19 -31 0.022 14.55 -2.062 0.0196 Indeterminate 0 35 35 0.05 10 1.224 0.55 0.5 2.102 -212 -2.326 69.74 -3.025 0.00124 Decreasing 0 32 32 0.1 31 3.428 0.711 0.5 8.29 120 2.326 61.32 1.941 0.0262 Indeterminate 0 35 35 0.5 480 76.19 43.56 41 103.5 55 2.326 70.37 0.767 0.221 Indeterminate 0 4 4 0.4 1 0.85 0.795 1 0.3 -3 0.375 2.236 -0.894 0.186 Indeterminate 0 4 4 4.95E-05 8.60E-04 3.17E-04 1.90E-04 1.80E-04 3.68E-04 6 0.042 2.944 1.698 0.0447 Indeterminate 0 4 4 0.0495 0.28 0.131 0.107 0.0975 0.102 0 0.625 2.944 N/A N/A Indeterminate 0 17 17 0.25 25 11.3 7.113 11 7.653 -48 0.023 24.18 -1.944 0.026 Indeterminate 0 7 7 0.2 13 5.314 3.151 5 4.506 4 0.281 6.583 0.456 0.324 Indeterminate 0 4 4 4100 56300 42125 28655 54050 25382 -2 0.375 2.944 -0.34 0.367 Indeterminate 0 17 17 60 1400 766.9 530.2 750 501 -90 0 24.18 -3.681 1.16E-04 Decreasing 0 14 14 0.08 4.5 1.53 0.877 0.75 1.485 34 0.031 18 1.833 0.0334 Indeterminate Notes Note 1 - nondetect values were replaced with 1/2 detection limits. ATTACHMENTS ATTACHMENT D-1 ESTIMATE OF TRANSPORT DISTANCES BASED ON DARCY FLUX SANTA SUSANA FIELD LABORATORY VENTURA COUNTY, CALIFORNIA ESTIMATE OF TRANSPORT DISTANCES BASED ON DARCY FLUX ATTACHMENT D-1 ATTACHMENT D-2 EEL CONCENTRATION TREND GRAPHS SSFL [eel] Analysis prepared on: 2/18/2015 Time Series ES-23 Detect 1,1-dichloroethene ND Significant Decreasing Trend Outlier u g / L 10.0 9.0 8.0 7.0 6.0 5.0 4.0 3.0 2.0 1.0 0.0 86 Trend test 88 90 92 94 96 Samples 98 00 02 04 06 08 10 02 04 06 08 10 Year Graph 1 ES-23 Detect Cis-1,2-dichloroethene ND Outlier u g / L Trend test 50. 45. 40. 35. 30. 25. 20. 15. 10. 5. 0. 86 88 90 92 94 Samples 96 98 00 Year Graph 2 Prepared by: MWH 1 SSFL [eel] Analysis prepared on: 2/18/2015 Time Series ES-23 Detect Trichloroethene ND Significant Decreasing Trend Outlier u g / L Trend test 1000. 900. 800. 700. 600. 500. 400. 300. 200. 100. 0. 86 88 90 92 94 Samples 96 98 00 02 04 06 08 10 Year Graph 3 Prepared by: MWH 2 SSFL [es-28] Analysis prepared on: 2/18/2015 Time Series ES-28 Detect 1,1-dichloroethene ND Outlier u g / L 5.00 4.50 4.00 3.50 3.00 2.50 2.00 1.50 1.00 0.50 0.00 87 Trend test 88 89 90 91 92 Samples 93 94 95 96 97 98 99 94 95 96 97 98 99 Year Graph 1 ES-28 Detect Trichloroethene ND Outlier u g / L Trend test 200. 180. 160. 140. 120. 100. 80. 60. 40. 20. 0. 87 88 89 90 91 Samples 92 93 Year Graph 2 Prepared by: MWH 1 SSFL [es-29] Analysis prepared on: 2/18/2015 Time Series ES-29 Detect 1,1-dichloroethene ND Significant Decreasing Trend Outlier u g / L 10.0 9.0 8.0 7.0 6.0 5.0 4.0 3.0 2.0 1.0 0.0 85 Trend test 90 95 Samples 00 05 10 15 05 10 15 Year Graph 1 ES-29 Detect Cis-1,2-dichloroethene ND Outlier u g / L Trend test 1.00 0.90 0.80 0.70 0.60 0.50 0.40 0.30 0.20 0.10 0.00 85 90 95 Samples 00 Year Graph 2 Prepared by: MWH 1 SSFL [es-29] Analysis prepared on: 2/18/2015 Time Series ES-29 Detect Nitrate-no3 ND Outlier m g / L 100. 90. 80. 70. 60. 50. 40. 30. 20. 10. 0. 85 Trend test 90 95 Samples 00 05 10 15 05 10 15 Year Graph 3 ES-29 Detect Trichloroethene ND Outlier u g / L Trend test 100. 90. 80. 70. 60. 50. 40. 30. 20. 10. 0. 85 90 95 Samples 00 Year Graph 4 Prepared by: MWH 2 SSFL [es-30] Analysis prepared on: 2/18/2015 Time Series ES-30 Detect 1,1-dichloroethene ND Significant Decreasing Trend Outlier u g / L 10.0 9.0 8.0 7.0 6.0 5.0 4.0 3.0 2.0 1.0 0.0 86 Trend test 88 90 92 94 96 Samples 98 00 02 04 06 08 10 12 02 04 06 08 10 12 Year Graph 1 ES-30 Detect Cis-1,2-dichloroethene ND Outlier u g / L Trend test 50. 45. 40. 35. 30. 25. 20. 15. 10. 5. 0. 86 88 90 92 94 Samples 96 98 00 Year Graph 2 Prepared by: MWH 1 SSFL [es-30] Analysis prepared on: 2/18/2015 Time Series ES-30 Detect Trichloroethene ND Outlier u g / L Trend test 500. 450. 400. 350. 300. 250. 200. 150. 100. 50. 0. 86 88 90 92 94 Samples 96 98 00 02 04 06 08 10 12 Year Graph 3 Prepared by: MWH 2 SSFL [pz-050] Analysis prepared on: 2/18/2015 Time Series PZ-050 Detect Bis(2-ethylhexyl) phthalate ND Outlier u g / L 1.00 0.90 0.80 0.70 0.60 0.50 0.40 0.30 0.20 0.10 0.00 08 Trend test 09 10 11 Samples 12 13 14 15 13 14 15 Year Graph 1 PZ-050 Detect Cadmium, dissolved ND Outlier m g / L Trend test 0.0010 0.0009 0.0008 0.0007 0.0006 0.0005 0.0004 0.0003 0.0002 0.0001 0.0000 08 09 10 Samples 11 12 Year Graph 2 Prepared by: MWH 1 SSFL [pz-050] Analysis prepared on: 2/18/2015 Time Series PZ-050 Detect Diesel range organics (c21-c30) ND Outlier m g / L Trend test 0.5000 0.4500 0.4000 0.3500 0.3000 0.2500 0.2000 0.1500 0.1000 0.0500 0.0000 08 09 10 Samples 11 12 13 14 15 Year Graph 3 Prepared by: MWH 2 SSFL [rs-15] Analysis prepared on: 2/18/2015 Time Series RS-15 Detect 1,1-dichloroethene ND Outlier u g / L 50. 45. 40. 35. 30. 25. 20. 15. 10. 5. 0. 85 Trend test 90 95 Samples 00 05 10 15 05 10 15 Year Graph 1 RS-15 Detect Cis-1,2-dichloroethene ND Outlier u g / L Trend test 20.0 18.0 16.0 14.0 12.0 10.0 8.0 6.0 4.0 2.0 0.0 85 90 95 Samples 00 Year Graph 2 Prepared by: MWH 1 SSFL [rs-15] Analysis prepared on: 2/18/2015 Time Series RS-15 Detect Nitrate-no3 ND Outlier m g / L 100. 90. 80. 70. 60. 50. 40. 30. 20. 10. 0. 85 Trend test 90 95 Samples 00 05 10 15 05 10 15 Year Graph 3 RS-15 Detect Trichloroethene ND Significant Decreasing Trend Outlier u g / L Trend test 2000. 1800. 1600. 1400. 1200. 1000. 800. 600. 400. 200. 0. 85 90 95 Samples 00 Year Graph 4 Prepared by: MWH 2 SSFL [rs-17] Analysis prepared on: 2/18/2015 Time Series RS-17 Detect Trichloroethene ND Outlier u g / L Trend test 5.00 4.50 4.00 3.50 3.00 2.50 2.00 1.50 1.00 0.50 0.00 85 90 95 Samples 00 05 10 15 Year Graph 1 Prepared by: MWH 1 Appendix Human Health and Ecological Risk Assessment Findings for EEL RFI Site Appendix E1 HHRA APPENDIX E1  Human Health Risk Assessment for the Environmental Effects Laboratory RFI Site 1.0 Introduction This appendix provides the results of the human health risk assessment (HHRA) for the Environmental  Effects Laboratory (EEL) Resource Conservation and Recovery Act facility investigation (RFI) site (the portion  of the site located within Administrative Area III only) in Boeing RFI Subarea 5/9 South at the Santa Susana  Field Laboratory (SSFL) in Ventura County, California. The objective of this HHRA is to determine whether  exposure to the environmental media at the site could pose unacceptable risks to human health and  requires evaluation of corrective action as part of a corrective measure study (CMS), or whether potential  risks to human receptors exposed to current concentrations of chemicals in environmental media are  acceptable. If current concentrations of chemicals in environmental media at the site pose unacceptable  human health risks and CMS areas are identified, this HHRA confirms that the areas of the site outside of  identified CMS areas would be eligible for a no further action (NFA) designation. Appendix E2 provides the  results of the ecological risk assessment (ERA) for the EEL RFI site. Appendix E3 provides the identification of  CMS and NFA areas based on the HHRA and ERA results. Additional data were collected by United States  Department of Energy and provided to Boeing after preparation of the EEL DSFR had commenced; these  data were not included in the risk assessments presented in Appendices E1 through E3 and are evaluated in  a qualitative nature only in Appendix E4.  This HHRA was performed following the methods and assumptions described in the Final Standardized Risk  Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory, Ventura County, California  (SRAM Rev. 2 Addendum) (MWH, 2014a) and the Integration of the Surficial Media Operable Unit Risk  Assessment Methodology and the Data Quality Objectives Process, Boeing RCRA Facility Investigation, Santa  Susana Field Laboratory, Ventura County, California (CH2M HILL, 2013a), which was submitted as  Appendix C of the Comprehensive Data Quality Objectives Report. Chemical and radiological sampling  results for environmental media at the EEL RFI site were used to estimate potential risks and hazards for  current and potential future human receptors and to identify risk drivers contributing to unacceptable risks  and hazards, if any.  2.0 Background 3.0 Organization The EEL RFI site is located on the boundary between Administrative Areas III and IV in the western portion of  the SSFL (refer to Figure 1‐1 of this EEL RFI site Data Summary and Findings Report [EEL DSFR]). As described  in this EEL DSFR, the Boeing RFI and this risk assessment pertain to that portion of EEL within Area III. The  site is currently inactive, and all structures have been demolished. A summary of the site history and existing  conditions is provided in Section 2 of this EEL DSFR. Additional detailed information on the historical use and  site conditions at the EEL RFI site are presented in the Group 5 – Central Portions of Areas III and IV RCRA  Facility Investigation Report, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2008)  and the Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI Subarea 5/9  South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2013b).  This HHRA includes the following components:    Data Used for the HHRA (Section 4.0). This section presents the process for selecting  chemical/radionuclide data to include in the HHRA.  EN0411151012BAO 1 APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE  Chemicals and Radionuclides of Potential Concern (Section 5.0). This section identifies the  chewmicals/radionuclides that are the focus of the human health risk quantification process.   Human Exposure Assessment (Section 6.0). This section identifies the pathways of potential human  exposure that are considered in the HHRA and presents the exposure point concentrations (EPCs) for  soil and soil vapor at the EEL RFI site.   Human Toxicity Assessment (Section 7.0). This section summarizes the toxicity of the selected  chemicals and the relationship between magnitude of exposure and the occurrence of adverse health  effects.   Human Health Risk Characterization (Section 8.0). This section summarizes the risks to human health  from potential exposure to chemicals/radionuclides in environmental media.   Summary of the HHRA (Section 9.0). This section summarizes the results of the HHRA.   Uncertainties Associated with the HHRA (Section 10.0). This section discusses the uncertainties and  assumptions associated with the HHRA.  References cited in this appendix are included in Section 11.0 of this appendix.   4.0 Data Used for the HHRA Table 3‐1 of this EEL DSFR summarizes the nature and extent and fate and transport evaluations performed  for soil, soil vapor, and vadose zone bedrock at the EEL RFI site. Figures 4‐1 through 4‐5 of this EEL DSFR  present summaries of the soil and soil vapor characterization that has been performed to date at the EEL RFI  site. Table 3‐2 of this EEL DSFR summarizes the nature and extent and fate and transport evaluations  performed for groundwater beneath and downgradient from the EEL RFI site. Figure 4‐7 of this EEL DSFR  presents the estimated footprint of impacted groundwater at the EEL RFI site.   Table 1 of Attachment 1 to this appendix provides a summary of the soil and soil vapor samples used for this  HHRA by medium, sample ID, date of collection, sampling depth interval, and target receptor types. The risk  estimate associated with Chatsworth Formation groundwater is represented for the entire Boeing RFI  Subarea 5/9 South using detected concentrations from the maximum risk well point (HAR‐18), as described  in Appendix C of the Boeing RFI Subarea 5/9 South Data Summary and Findings Report (5/9S DSFR).  4.1 Data Evaluation and Selection Criteria In accordance with the processes outlined in the SRAM Rev. 2 Addendum (MWH, 2014a), available site data  were reviewed to identify a set of data of acceptable quality for this HHRA. In addition to the steps normally  included during standard data validation procedures, the following steps were followed in generating the  final risk assessment data set:   1. Estimated values (flagged with a “J” qualifier) were treated as detected concentrations.   2. Soil and soil vapor samples collected from depths greater than 10 feet below ground surface (bgs) were  removed from the data set, per the SRAM Rev. 2 Addendum.  3. Where field duplicates were collected, the maximum detected result between the duplicate and the  original sample was selected. If there was one detection and one nondetection in the duplicate pair, the  detected value was selected. If both were nondetects, the lowest value was selected.  4. The shallowest soil vapor data from between 51 to 10 feet bgs were used for each sample point.                                                               1 In some cases, soil vapor data from slightly shallower than 5 feet bgs may be included if deemed to provide important spatial coverage. No soil  vapor data shallower than 5 feet bgs were included for the EEL RFI site.  2 EN0411151012BAO 5.0 APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE Chemicals and Radionuclides of Potential Concern Chemicals of potential concern (COPCs) are those chemicals that are carried through the human health risk  quantification process. Radionuclides carried through the HHRA are referred to as radionuclides of potential  concern (ROPCs). This section summarizes the chemicals/radionuclides identified as COPCs/ROPCs in soil  and soil vapor at the EEL RFI site. The process for selection of COPCs/ROPCs for Chatsworth Formation  groundwater is described in Appendix C of the 5/9S DSFR. During the course of the HHRA, the COPCs/ROPCs  are evaluated to identify and prioritize which constituents, if any, are estimated to pose unacceptable risks.  COPCs/ROPCs were identified in accordance with the process described in the SRAM Rev. 2 Addendum  (MWH, 2014a).   The following sequential criteria were applied to select COPCs/ROPCs for the EEL RFI site:   The chemical/radionuclide was detected at the EEL RFI site using validated laboratory analyses.    The chemical/radionuclide was present in excess of concentrations observed in laboratory or field  blanks.   The measured concentration was in excess of soil background values. For this comparison, the following  decision rules were used:   If the maximum detection was below the background comparison value (95/95 upper threshold limit  [UTL] for soil2), then that chemical was not considered a COPC/ROPC.   If the maximum detection exceeded two times the background comparison value, then that  chemical was identified as a COPC/ROPC, per Appendix J of the SRAM Rev. 2 Addendum.   If the maximum detection was above the background comparison value but below two times that  value, a more rigorous statistical evaluation was conducted to determine whether the population of  site data was statistically different than the background population, as described in Section 3.3 of  the SRAM Rev. 2 Addendum.   Tables 2 and 3 of Attachment 1 to this appendix provide the results of the screening of maximum soil  concentrations against background comparison values and two times background comparison values for  detected chemicals and radionuclides, respectively. The results of the population statistical comparisons of  EEL RFI site soil concentrations with background comparison values are provided in Table 4 of Attachment 1  to this appendix. Table E1‐1 lists the final human health COPCs identified for soil and soil vapor at the EEL  RFI site. The table also provides summary statistics for soil collected from 0 to 2 feet bgs and from 0 to  10 feet bgs and for soil vapor.   Table E1‐2 lists the final human health ROPCs and summary statistics identified for radionuclides in soil at  the EEL RFI site.  6.0 Human Exposure Assessment The exposure assessment component of this HHRA describes the means by which people at or near the site  may come into contact with chemicals/radionuclides in soil, soil vapor, and groundwater. The conceptual  site model (CSM) identifies the potential human exposures that are being considered for this risk  assessment. Figure E1‐1 depicts the CSM for the EEL RFI site based on the generalized CSM provided in the  SRAM Rev. 2 Addendum.  Since Boeing plans for the future use of its property as open space, the most likely future use of SSFL is for  recreational purposes, and recreational users are the most plausible future human receptors. Therefore, risk  estimates for future recreational scenarios are quantified in this HHRA. Boeing has also elected to assess                                                               2 Based on data from the Final Chemical Soil Background Study Report (DTSC, 2012a) and Combined‐Data Background Threshold Values and  Methodology Narrative Chemical Soil Background Study (DTSC, 2012b).  EN0411151012BAO 3 APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE potential risks for a hypothetical suburban resident to provide conservative estimates for CMS planning;  therefore, this exposure pathway is also depicted in Figure E1‐1.  The potential exposure scenarios considered for this HHRA include the following:   Hypothetical Suburban Resident – Soil Contact: Potential exposure of suburban residents to  constituents in soil down to 10 feet bgs3 by incidental ingestion, dermal contact, and inhalation of dust  and vapors.   Hypothetical Suburban Resident – Garden Use: Potential uptake of constituents in soil to 2 feet bgs into  homegrown produce and consumption of produce by suburban residents.    Hypothetical Suburban Resident – Indoor Air: Potential inhalation exposure of hypothetical suburban  residents to constituents volatilizing from soil vapor to indoor.   Hypothetical Suburban Resident – Groundwater Use: Potential domestic use of groundwater.    Future Recreator: Potential exposure of future recreators to constituents in soil to 2 feet bgs by  incidental ingestion, dermal contact, and inhalation of dust and vapors.   6.1 Exposure Point Concentrations EPCs are conservative estimates of constituent concentrations that a receptor may come into contact with  and are specific to each exposure medium. For routes of exposure to soil, soil vapor, and groundwater, EPCs  are calculated using concentrations directly measured in soil, soil vapor, or groundwater samples collected  during field investigations at Boeing RFI Subarea 5/9 South. EPCs were computed using the methods  described in the SRAM Rev. 2 Addendum and are represented by either the upper confidence limit (UCL) on  the mean concentration (as recommended by ProUCL) or the maximum concentration, whichever is lowest.  The EPC is therefore considered a conservative upper‐bound estimate that is not likely to underestimate the  mean concentration.  Polychlorinated biphenyl (PCB) congener concentrations in soil were estimated based on detected  Aroclor‐1254 and ‐1260 concentrations, using the extrapolation factor approach as described in the SRAM  Rev. 2 Addendum (MWH, 2014a). From this, the total 2,3,7,8‐TCDD toxicity equivalents (TEQs) and risks for  PCB congeners were estimated. The results of the extrapolation calculations are provided in Table 5 of  Attachment 1 to this appendix.  The risk estimate associated with Chatsworth Formation groundwater is represented for the entire Boeing  RFI Subarea 5/9 South using detected concentrations from the maximum risk well point (HAR‐18), as  described in Appendix C of the 5/9S DSFR. For each COPC, the maximum concentration detected over the  last 3 years of available data was used as the EPC. When inorganics data were reported for both dissolved  and total forms (from filtered or unfiltered samples), the highest value was selected as the EPC.  EPCs for COPCs in soil (0 to 2 feet bgs and 0 to 10 feet bgs) and soil vapor are summarized for the EEL RFI site  in Table E1‐1. EPCs for ROPCs are summarized in Table E1‐2.  7.0 Human Toxicity Assessment The toxicity assessment component of this HHRA identifies the types of toxic effects a chemical can exert.  COPCs are divided into two broad groups on the basis of their effects on human health: noncarcinogens and  carcinogens. This division is made because health risks are calculated quite differently for carcinogenic and  noncarcinogenic effects, and separate toxicity values have been developed for these effects. Carcinogens  are those chemicals suspected of causing cancer following exposure; noncarcinogenic effects cover a wide  variety of systemic effects, such as liver toxicity or developmental effects. Some chemicals (such as                                                               3 In accordance with the SRAM Rev. 2 Addendum, risk estimates for residential scenarios were estimated for both the 0‐to‐2‐foot‐bgs and 0‐to‐10‐ foot‐bgs depth intervals and the interval exhibiting the higher risk is reported for each RFI site.  4 EN0411151012BAO APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE naphthalene) are capable of eliciting both carcinogenic and noncarcinogenic responses; therefore, these  carcinogens are also evaluated for systemic (noncarcinogenic) effects.   The risk‐based screening levels (RBSLs) used in this HHRA for assessing cancer risk and/or noncancer hazard  incorporate these toxicity values, which are route‐specific. Toxicity values for the RBSL calculations were  obtained from the general hierarchy of toxicity information sources described in Section 3.3 of Attachment 1  of Appendix B of the SRAM Rev. 2 Addendum (MWH, 2014a). Since the SRAM Rev. 2 Addendum was  completed, additional chemicals and radionuclides without RBSLs have been detected that required  derivation of RBSLs for use in this and other risk assessments for SSFL RFI sites. These are provided in  Attachment 2 of this appendix.  8.0 Human Health Risk Characterization This subsection provides the quantitative risk characterization results for soil, soil vapor, and groundwater  samples used in the HHRA. Risks and hazards from exposures to soil by hypothetical suburban residents and  future recreators were evaluated using a sum‐of‐fractions (SOF) approach, as described in the SRAM Rev. 2  Addendum. Indoor air exposures to soil vapor by suburban residents were also evaluated using the SOF  approach. Potential exposures from domestic use of Chatsworth Formation groundwater by suburban  residents were evaluated using the approach described in Appendix C of the 5/9S DSFR.  Potential site‐related risks are estimated in this HHRA by calculating ‘incremental’ risks. Incremental risk is  defined as that portion of the site risk in excess of that resulting from background/ambient concentrations  of chemicals found in soil at the EEL RFI site. Incremental risk is therefore a measure of risks attributable to  site‐related releases. Background risk was estimated using the UCL on the mean for background  concentrations.  8.1 Summary of Risk Estimates by Exposure Scenario This section summarizes the risk estimates for the exposure scenarios evaluated at the EEL RFI site:    Hypothetical suburban residential scenario  Future recreational scenario  Each of these exposure scenarios was evaluated using the exposure assumptions and methods described in  the SRAM Rev. 2 Addendum (MWH, 2014a).  8.1.1 Hypothetical Suburban Residential Exposure Scenario Potential suburban residential exposure to COPCs and ROPCs in soil, soil vapor, and groundwater were  evaluated under this scenario. The results are described by exposure medium in the following subsections,  and summarized in Table E1‐3. Since suburban residents could potentially be exposed to more than one  environmental medium, multimedia risk estimates are also computed by summing the medium‐specific  risks, where appropriate.  8.1.1.1 Direct Contact with Soil  Exposure to COPCs in Soil   Potential routes of exposure to COPCs from direct contact with soil include incidental ingestion, dermal  contact, and inhalation of fugitive dust and vapors emitted from soil to ambient air. The excess lifetime  cancer risk (ELCR) and hazard index (HI) estimates for the suburban resident exposure scenario, derived  using the SOF approach, are summarized in Table E1‐3. In accordance with the SRAM Rev. 2 Addendum, the  0‐to‐2‐foot‐bgs or 0‐to‐10‐foot‐bgs soil interval resulting in the highest risk and/or hazard estimates was  used. The risk calculations for the 0‐to‐2‐foot‐bgs soil interval are provided in Table E1‐5. The risk  calculations for the 0‐to‐10‐foot‐bgs soil interval are provided in Table 6 of Attachment 1 to this appendix.  For the EEL RFI site, the risk estimates for the 0‐to‐2‐foot‐bgs interval are higher and therefore were used  EN0411151012BAO 5 APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE for computation of incremental risk. The risk calculation table for background soil4 is provided in Table E1‐6.  The chemical‐specific incremental risks and hazards for COPCs detected in soil are provided in Table E1‐7.  For the direct soil contact pathway, the total site ELCR is 4 x 10‐4 and the incremental risk is 3 x 10‐4, which is  above the United States Environmental Protection Agency (USEPA) target risk range of 1 x 10‐6 to 1 x 10‐4  and exceeds the DTSC point of departure of 1 x 10‐6. The primary risk driver to the incremental soil ELCR is  arsenic (92 percent contribution; 2 x 10‐4 risk), with minor contributions from 2,3,7,8‐TCDD TEQ (4 percent  contribution; 1 x 10‐5 risk); and benzo(a)pyrene (2 percent contribution; 5 x 10‐6 risk). A statistical  comparison of arsenic levels at the EEL RFI site (site EPC of 26.4 milligrams per kilogram [mg/kg] and  maximum detected value of 110 mg/kg) with background concentrations indicates that onsite arsenic levels  are statistically higher than background.  The total site HI for soil for this scenario is 2 and the incremental HI is also 2, which exceeds the USEPA and  DTSC threshold HI value of 1. Primary contributors to the incremental soil HI are 2,3,7,8‐TCDD TEQ (55  percent contribution; hazard quotient [HQ] = 1) and arsenic (38 percent contribution; HQ = 0.7). However,  since 2,3,7,8‐TCDD TEQ and arsenic do not have the same critical toxic endpoint, and no individual chemical  HQ exceeds 1, no unacceptable hazard is identified.  The potential risks from exposure to lead in soil at the EEL RFI site were not evaluated since lead was not  identified as a COPC. A statistical comparison of lead levels with background concentrations indicates that  onsite lead levels are not statistically higher than background.  Exposure to ROPCs in Soil  The risk estimates for ROPCs identified for soil were calculated separately from those associated with  COPCs. Potential routes of exposure to ROPCs from direct contact with soil include incidental ingestion,  inhalation of fugitive dust, and external exposure. For the EEL RFI site, ROPCs are the same for the 0‐to‐2‐ foot‐bgs and the 0‐to‐10‐foot‐bgs interval. The ELCR estimates for the suburban resident exposure scenario,  derived using the SOF approach, are summarized in Table E1‐4. The risk calculations for the 0‐to‐2‐foot‐bgs  soil interval are provided in Table E1‐8.   For the direct contact with soil pathway, the total site ELCR is 2 x 10‐7, which is below the USEPA target risk  range of 1 x 10‐6 to 1 x 10‐4 and below the DTSC point of departure of 1 x 10‐6.  8.1.1.2 Garden Use  Another pathway evaluated for the hypothetical future suburban resident is the consumption of  homegrown produce that has accumulated COPCs from soil. In accordance with the SRAM Rev. 2  Addendum, only the 0‐to‐2‐foot‐bgs soil interval is considered for this scenario. The risk calculation results  for the homegrown produce exposure pathway are provided in Table E1‐5. The risk calculation table for  background soil is provided in Table E1‐6.  For the homegrown produce consumption pathway, the total site ELCR is 3 x 10‐1 and the incremental risk is  2 x 10‐1, which is above the USEPA target risk range of 1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of  departure of 1 x 10‐6. The primary risk driver (Table E1‐5) is arsenic (96 percent contribution; 3 x 10‐1 risk),  with minor contributions from 2,3,7,8‐TCDD TEQ (2 percent contribution; 7 x 10‐3 risk); and carcinogenic  polycyclic aromatic hydrocarbons (PAHs; 1 percent contribution; 4 x 10‐3 risk).  The total site HI for this scenario is 486, and the incremental HI is 377, which exceeds the USEPA and DTSC  threshold HI value of 1. Primary contributors to the site soil HI (Table E1‐5) are arsenic (52 percent  contribution; HQ = 253) and 2,3,7,8‐TCDD TEQ (42 percent contribution; HQ = 206). HQs also exceeded 1 for  2‐methyl‐4‐chlorophenoxyacetic acid (HQ = 7), Aroclor‐1254 (HQ = 7), antimony (HQ = 6), and Aroclor‐1260  (HQ = 5).                                                               4 Only COPCs identified for soil at the EEL RFI site are included in the background risk and hazard evaluations.  6 EN0411151012BAO APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE As described in the SRAM Addendum (MWH, 2014a), estimated risks for this pathway are calculated  separately because of the high uncertainties associated with modeling the uptake of chemicals in soil by  plants.  8.1.1.3 Indoor Air Pathway  For the indoor air pathway, the potential route of exposure to volatile COPCs detected in soil vapor is  inhalation of volatile chemicals that could migrate from the vadose zone to inside a future residence. The  vapor intrusion pathway evaluation for the EEL RFI site was performed in accordance with the  Recommended Approach for Assessing the Vapor Intrusion Pathway, Boeing RFI Facility Investigation Project,  Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2013c; Appendix A to the  Comprehensive Data Quality Objectives Report). The ELCR and HI estimates for the suburban resident  exposure scenario, derived using the SOF approach, are summarized in Table E1‐3, and the risk calculation  table is provided in Table E1‐9.  For the indoor air pathway, the total site ELCR is 3 x 10‐5, which is within the USEPA target risk range of  1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of departure of 1 x 10‐6. The primary risk drivers are  trichloroethene (TCE) (94 percent contribution; ELCR=3 x 10‐5) and benzene (6 percent contribution; ELCR=2  x 10‐6).   The total site HI for is 7 for this scenario, which exceeds the USEPA and DTSC threshold HI value of 1.  The primary contributor to the site HI is TCE (>99 percent contribution; HQ = 7).  8.1.1.4 Groundwater Use Pathway  Exposure to COPCs in Groundwater  Potential routes of exposure to COPCs in Chatsworth Formation groundwater include ingestion, dermal  contact, and inhalation of vapors during assumed hypothetical domestic use. Risks and hazards from  groundwater use were evaluated using the approach described in Appendix C of the 5/9S DSFR. Results  provided here for Chatsworth Formation groundwater are based on the maximum risk well within Boeing  RFI Subarea 5/9 South (at HAR‐18), using the maximum concentrations detected over the most recent 3  years of available data. The ELCR and HI estimates for the suburban residential exposure scenario are  summarized in Table E1‐3, and the risk calculation table is provided in Table E1‐10.  For groundwater use at Chatsworth Formation well HAR‐18, the ELCR is 3 x 10‐2, which is above the USEPA  target risk range of 1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of departure of 1 x 10‐6. The primary risk  drivers are vinyl chloride (87 percent contribution; 3 x 10‐2 risk); n‐nitrosodimethylamine (8 percent  contribution; 2 x 10‐3 risk); and TCE (5 percent contribution; 2 x 10‐3 risk).  The HI is 426 for this scenario, which exceeds the USEPA and DTSC threshold HI value of 1. The primary  contributors to the HI are TCE (54 percent contribution; HQ = 230); cis‐1,2‐dichloroethene (38 percent  contribution; HQ = 163); n‐nitrosodimethylamine (5 percent contribution; HQ = 23); and vinyl chloride  (2 percent contribution; HQ = 8).  The potential risk from exposure to lead in groundwater is evaluated separately from other carcinogens and  noncarcinogens. For this HHRA, potential risk from lead is evaluated by comparing the maximum EPC for  lead in Chatsworth Formation groundwater to the USEPA Action Level in water 15 µg/L. Only one of the 10  well points in Boeing RFI Subarea 5/9 South had an EPC exceeding 15 µg/L, at well point RD‐55A where the  EPC was 40.1 µg/L.  Exposure to Radionuclides in Groundwater  The risk estimates for ROPCs identified for Chatsworth Formation groundwater (at HAR‐18) were calculated  separately from those associated with COPCs. The risk calculation table provided in Table E1‐11 indicates  that the ELCR is 2 x 10‐5, which is within the USEPA target risk range of 1 x 10‐6 to 1 x 10‐4 and exceeds the  EN0411151012BAO 7 APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE DTSC point of departure of 1 x 10‐6. The main contributor to the ELCR is uranium‐233/234 (94 percent  contribution; 1 x 10‐5 risk).  8.1.2 Future Recreational Exposure Scenario Since Boeing plans for the future use of its property as open space, the most likely future human use of SSFL  is for recreational purposes. Potential recreational exposure to COPCs in soil is evaluated under this  scenario. The results are described in the following subsections.  8.1.2.1 Direct Contact with Soil  Exposure to COPCs in Soil  Potential routes of exposure to COPCs from direct contact with soil include incidental ingestion, dermal  contact, and inhalation of fugitive dust and vapors emitting from soil to ambient air. In accordance with the  SRAM Rev. 2 Addendum, only the 0‐to‐2‐foot‐bgs soil interval is considered for this scenario. The ELCR and  HI estimates for the future recreational exposure scenario, derived using the SOF approach, are summarized  in Table E1‐3. The risk calculation results for site soil and background soil are provided in Table E1‐5 and  Table E1‐6, respectively. The chemical‐specific incremental risks and hazards for this exposure scenario are  provided in Table E1‐7.  For the direct soil contact pathway, the total site ELCR is 1 x 10‐4, and the incremental risk is 7 x 10‐5, which  does not exceed the USEPA target risk range of 1 x 10‐6 to 1 x 10‐4 and exceeds the DTSC point of departure  of 1 x 10‐6. The primary risk driver to the incremental soil ELCR is arsenic (91 percent contribution; 6 x 10‐5  risk), with minor contributions from 2,3,7,8‐TCDD TEQ (4 percent contribution; 3 x 10‐6 risk) and  benzo(a)pyrene (3 percent contribution; 2 x 10‐6 risk). A statistical comparison of arsenic levels at the EEL RFI  site (EPC of 26.4 mg/kg and maximum detected value of 110 mg/kg) with background concentrations  indicates that onsite arsenic levels are statistically higher than background.   The total site HI for soil for this scenario is 0.4 and the incremental HI is 0.3, which is below the USEPA and  DTSC threshold HI value of 1.  The potential risks from exposure to lead in soil at the EEL RFI site were not evaluated since lead was not  identified as a COPC. A statistical comparison of lead levels with background concentrations indicates that  onsite lead levels are not statistically higher than background.  Exposure to ROPCs in Soil  The risk estimates for ROPCs identified for soil were calculated separately from those associated with  COPCs. The ELCR estimate for the recreational exposure scenario, derived using the SOF approach, is  summarized in Table E1‐4. The risk calculations for the 0‐to‐2‐foot‐bgs soil interval are provided in Table E1‐ 8.   For the direct contact with soil pathway, the total site ELCR is 4 x 10‐8, which is below the USEPA target risk  range of 1 x 10‐6 to 1 x 10‐4 and below the DTSC point of departure of 1 x 10‐6.  8.2 Evaluation of Potential for Hot Spots in Soil An additional evaluation was conducted to determine the potential for localized areas where higher  constituent concentrations (that is, potential hot spots) could occur and to determine whether these may  represent additional areas that warrant evaluation in the CMS.   The soil hot‐spot evaluation was conducted using the approach outlined in Hot Spot Evaluation Technical  Memorandum Prepared for the Santa Susana Field Laboratory, Ventura County, California ‐ Technical  Memorandum (MWH, 2014b; Appendix J of the SRAM Rev. 2 Addendum). To identify hot spots, maximum  detected COPC concentrations in soil 0 to 10 feet bgs were compared with 10 times the most conservative  human health RBSL. The use of 10 times the most conservative human health RBSL identifies any portion of  an RFI site that is within USEPA’s risk management range of 10‐6 to 10‐4 for carcinogens and at a level  typically associated with a lowest adverse effect level for noncarcinogens. As indicated in Table 7 of  8 EN0411151012BAO APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE Attachment 1 to this appendix, the COPCs identified as potential soil hot‐spot chemicals at the EEL RFI site  include arsenic; 2,3,7,8‐TCDD TEQ; and benzo(a)pyrene. Since these COPCs are already identified for  evaluation in the CMS based on the HHRA results, no additional chemicals or areas are identified based on  this hot‐spot evaluation.  9.0 Summary of Human Health Risk Assessment 9.1 Hypothetical Suburban Residential Scenario This HHRA for the EEL RFI site was conducted in accordance with risk assessment methods and procedures  provided in the SRAM Rev. 2 Addendum (MWH, 2014a). The exposure scenarios evaluated included those  for the hypothetical future suburban residential and future recreational receptors. Chemicals/radionuclides  of concern (COCs/ROCs) are those COPCs/ROPCs identified during the HHRA as primary contributors posing  unacceptable risks and/or hazards and therefore are retained for further evaluation during the CMS. For this  HHRA, COCs are identified for soil and soil vapor only. COCs for groundwater are identified at the subarea  scale and are described further in the 5/9S DSFR. No ROCs are identified for soil at the EEL RFI site.  Potential suburban residential exposure to COPCs/ROPCs in soil, soil vapor, and groundwater are evaluated  under this scenario. The ELCR and HI results are summarized by exposure medium in Table E1‐3 for COPCs  and Table E1‐4 for ROPCs. Since suburban residents could potentially be exposed to more than one  environmental medium, multimedia risk estimates are also calculated by summing the medium‐specific  risks, where appropriate.  The following is a list of COCs identified for the hypothetical suburban residential exposure scenario at the  EEL RFI site, based on the ELCR and HI estimates:   Soil: Arsenic, 2,3,7,8‐TCDD TEQ, and benzo(a)pyrene were identified as COCs for direct contact with soil  by suburban residents.   Soil Vapor: TCE and benzene were identified as a COC for inhalation of indoor air by future residents.   Chatsworth Groundwater: COCs are identified at the subarea scale and are described further in the 5/9S  DSFR.  Although the risks associated with the plant consumption pathway and with extrapolated PCB congeners  were estimated in this HHRA, they were not considered for identification of COCs because of the high  uncertainties associated with the plant uptake modeling and PCB extrapolation approaches (MWH, 2014a).  9.2 Future Recreator Scenario Since Boeing plans for the future use of its property as open space, the most likely future human use of SSFL  is recreational. Potential recreational exposure to COPCs/ROPCs in soil is evaluated under this scenario. The  ELCR and HI results are summarized in Table E1‐3. The following is a list of COCs identified for the future  recreational exposure scenario at the EEL RFI site based on the ELCR and HI estimates:   Soil: Arsenic; 2,3,7,8‐TCDD TEQ; and benzo(a)pyrene were identified as COCs for direct contact with soil  by future recreators.  Appendix E3 provides the identification of CMS and NFA areas based on the HHRA and ERA results.  10.0 Uncertainties Associated with the HHRA Uncertainties associated with the results of the HHRA are a function of both the “state of the practice” of  risk assessment in general and uncertainty factors specific to an RFI site. The EEL RFI site HHRA is subject to  uncertainty with regard to a variety of factors that include:     Environmental sampling and analysis  Fate and transport estimation  Exposure assessment  EN0411151012BAO 9 APPENDIX E1 HUMAN HEALTH RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE   Toxicity assessment  Risk characterization  Uncertainties specific to the EEL RFI site are summarized in Table E1‐12.  11.0 References California Environmental Protection Agency, Department of Toxic Substances Control (DTSC). 2007. Consent  Order for Corrective Action, In the Matter of: Santa Susana Field Laboratory, Simi Hills, Ventura County,  California, The Boeing Company, National Aeronautics and Space Administration, and The U.S. Department  of Energy (Respondents). Docket No. P3‐07/08‐003. August 16.  California Environmental Protection Agency, Department of Toxic Substances Control (DTSC). 2012a. Final  Chemical Soil Background Study Report. December.  California Environmental Protection Agency, Department of Toxic Substances Control (DTSC). 2012b.  Combined‐Data Background Threshold Values and Methodology Narrative Chemical Soil Background Study.  December.  CH2M HILL. 2008. Group 5 – Central Portions of Areas III and IV RCRA Facility Investigation Report, Santa  Susana Field Laboratory, Ventura County, California. November.  CH2M HILL. 2013a. Integration of the Surficial Media Operable Unit Risk Assessment Methodology and the  Data Quality Objectives Process, Boeing RCRA Facility Investigation, Santa Susana Field Laboratory, Ventura  County, California. March 8.  CH2M HILL. 2013b. Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI  Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California. May.  CH2M HILL. 2013c. Recommended Approach for Assessing the Vapor Intrusion Pathway, Boeing RFI Facility  Investigation Project, Santa Susana Field Laboratory, Ventura County, California. March.  MWH. 2014a. Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field  Laboratory, Ventura County, California. August.  MWH. 2014b. Hot Spot Evaluation Technical Memorandum Prepared for the Santa Susana Field Laboratory,  Ventura County, California ‐ Technical Memorandum (Appendix J of the SRAM Rev. 2 Addendum (MWH,  2014a). August.  10 EN0411151012BAO Tables List of Tables E1‐1  E1‐2  E1‐3  E1‐4  E1‐5  E1‐6  E1‐7  E1‐8  E1‐9  E1‐10  E1‐11  Summary Statistics and Exposure Point Concentrations (EPCs) for Chemicals of Potential Concern  Summary Statistics and Exposure Point Concentrations (EPCs) for Radionuclides of Potential Concern  Chemical Risk Summary by Exposure Scenario  Radiological Risk Summary by Exposure Scenario  Risk and Hazard Estimates for Exposure to Soil (0 to 2 feet bgs)  Risk and Hazard Estimates for Exposure to Background Soil  Chemical‐specific Incremental Risk and Hazard Estimates for Soil  Risk Estimates for Exposure to Soil Radionuclides (0 to 2 feet bgs)  Risk and Hazard Estimates for Exposure to Soil Vapor  Risk and Hazard Estimates for Exposure to Chatsworth Groundwater (Domestic Use at Well HAR‐18)  Risk Estimates for Exposure to Radionuclides in Chatsworth Groundwater (Domestic Use at Well  HAR‐18)  E1‐12  Human Health Risk Assessment Uncertainty Analysis      EN0411151012BAO TABLE E1‐1 Summary Statistics and Exposure Point Concentrations (EPCs) for Chemicals of Potential Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Soil 0‐2 ft bgs  1‐Methyl naphthalene   2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   2‐Methylnaphthalene   4,4'‐DDD   4,4'‐DDE   4,4'‐DDT   Acenaphthene   Acenaphthylene   Aluminum   Anthracene   Antimony   Aroclor 1254   Aroclor 1260   Arsenic   Barium   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   Beryllium   beta‐BHC   bis(2‐Ethylhexyl) phthalate   Boron   Butyl benzyl phthalate   Cadmium   Chromium   Chrysene   Cobalt   Copper   Dibenzo(a,h)anthracene   Diethyl phthalate   Di‐n‐butyl phthalate   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Fluoranthene   Fluorene   Fluoride   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   Lead   Lithium   Manganese   MCPA   Mercury   Methylene chloride   Mirex   Molybdenum   m‐Xylene & p‐Xylene   Naphthalene   Nickel   Perchlorate   Phenanthrene  EN0317151003RDD Units Number of  Samples Number of  Detects Number of  Nondetects Percent  Detected mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 31 23 9 31 13 13 13 31 31 40 31 42 20 20 52 42 31 31 31 31 28 40 13 31 38 31 43 40 31 40 41 31 31 31 31 13 13 13 13 31 31 21 13 19 31 40 37 23 9 25 19 13 40 18 31 40 10 31 2 23 2 2 2 6 9 2 3 40 7 20 14 2 49 42 13 12 17 12 6 38 1 1 21 4 41 40 19 40 41 4 1 3 3 1 1 1 2 14 2 12 1 10 7 38 37 23 1 16 1 4 36 1 10 40 2 14 29 0 7 29 11 7 4 29 28 0 24 22 6 18 3 0 18 19 14 19 22 2 12 30 17 27 2 0 12 0 0 27 30 28 28 12 12 12 11 17 29 9 12 9 24 2 0 0 8 9 18 9 4 17 21 0 8 17 6% 100% 22% 6% 15% 46% 69% 6% 10% 100% 23% 48% 70% 10% 94% 100% 42% 39% 55% 39% 21% 95% 8% 3% 55% 13% 95% 100% 61% 100% 100% 13% 3% 10% 10% 8% 8% 8% 15% 45% 6% 57% 8% 53% 23% 95% 100% 100% 11% 64% 5% 31% 90% 6% 32% 100% 20% 45% Minimum Non  Maximum  Detect Nondetect 0.0034  NA  0.0107 0.0034 0.00284 0.00284 0.00284 0.0034 0.0034  NA  0.0034 0.173 0.0326 0.00712 10  NA  0.0034 0.0034 0.0034 0.0034 0.0034 0.06 0.00142 0.0342 1.87 0.0342 0.8  NA  0.0034  NA   NA  0.0034 0.0342 0.0342 0.0342 0.00142 0.00284 0.00284 0.00284 0.0034 0.0034 0.8 0.00142 0.34 0.0034 8.4  NA   NA  2.14 0.0114 0.0084 0.00142 1.03 0.0034 0.0034  NA  0.0082 0.0034 0.8  NA 0.05 0.8 0.034 0.034 0.004 0.8 0.8  NA 0.8 20 0.106 0.106 12  NA 0.8 0.042 0.042 0.042 0.042 2 0.02 0.8 20 0.36 2  NA 0.042  NA  NA 0.042 0.8 0.8 0.36 0.0166 0.034 0.034 0.034 0.8 0.8 11 0.0166 10 0.8 10  NA  NA 5.6 0.4 0.044 0.004 20 0.012 0.8  NA 0.012 0.8 Minimum  Detect Maximum  Detect  Mean Valuea 0.00094 4.47E‐09 0.018 0.0012 0.00035 0.0004 0.00053 0.00051 0.00048 4,440 0.00037 0.122 0.0047 0.00208 0.73 61 0.0002 0.00023 0.00043 0.00025 0.00097 0.16 0.00073 0.0287 1.1 0.00073 0.035 6 0.00033 1.8 4.5 0.00093 0.00597 0.0011 0.0044 0.00055 0.00055 0.0005 0.00047 0.00045 0.00089 0.2 0.00047 0.56 0.00093 1.8 8.5 217 0.94 0.0025 0.0027 0.0004 0.27 0.000372 0.00042 3 0.0039 0.00079 0.0012 0.0000519 0.032 0.0015 0.0018 0.0029 0.019 0.017 0.0021 33,200 0.13 7.5 0.099 0.046 110 189 1.2 0.74 1 0.23 0.52 1.3 0.00073 0.0287 9.99 0.013 0.751 32.9 1.5 12.7 25.6 0.096 0.00597 0.0023 0.099 0.00055 0.00055 0.0005 0.0011 2.3 0.015 3.1 0.00047 3.2 0.26 16.5 33.6 887 0.94 0.033 0.0027 0.0047 0.961 0.000372 0.0022 24.7 0.024 0.91 0.00107 0.0000107 0.0202 0.00135 0.00108 0.00139 0.00372 0.00123 0.00113 16,800 0.0051 0.482 0.0343 0.00452 13 113 0.0407 0.0257 0.0361 0.0095 0.0206 0.732 NA  NA  3.39 0.00441 0.227 20 0.0522 6.68 12.2 0.00458 NA  0.00157 0.0102 NA  NA  NA  0.000785 0.0783 0.0015 1.27 NA  0.843 0.0103 8.35 19.2 375 NA  0.0103 NA  0.00112 0.511 NA  0.00133 14.2 0.00591 0.0322  Standard Deviationa Exposure Point Concentrationb EPC Basis COPC 0.00013 0.0000139 0.00884 0.00015 0.000725 0.000858 0.00487 0.00336 0.000701 6,220 0.0232 1.14 0.0304 0.0101 21.9 24.3 0.212 0.13 0.176 0.0404 0.0961 0.244 NA  NA  2.68 0.00501 0.149 6.39 0.264 2.07 4.5 0.0168 NA  0.000525 0.017 NA  NA  NA  0.000315 0.406 0.00288 0.784 NA  0.652 0.0464 2.8 5.78 136 NA  0.00671 NA  0.00109 0.143 NA  0.000487 4.71 0.00603 0.16 ‐‐ 0.000021 0.032 ‐‐ 0.0018 ‐‐ 0.00637 0.0111 0.00197 ‐‐ 0.0507 0.791 0.0473 0.0379 26.4 ‐‐ 0.434 0.179 0.36 0.0568 0.219 ‐‐ 0.00073 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.538 ‐‐ ‐‐ 0.0105 ‐‐ ‐‐ 0.0176 0.00055 0.00055 0.0005 0.0011 0.831 0.0068 ‐‐ 0.00047 1.13 0.0675 ‐‐ ‐‐ ‐‐ 0.94 ‐‐ 0.0027 0.00184 ‐‐ ‐‐ 0.00161 ‐‐ 0.015 0.219 ‐‐ 95% Adjusted Gamma UCL  Maximum Result  ‐‐ Maximum Result  ‐‐ 95% KM (BCA) UCL  99% KM (Chebyshev) UCL  95% KM (t) UCL  ‐‐ 99% KM (Chebyshev) UCL  95% KM (t) UCL  95% KM (t) UCL  99% KM (Chebyshev) UCL  95% KM (Chebyshev) UCL  ‐‐ 99% KM (Chebyshev) UCL  97.5% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  97.5% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 99% KM (Chebyshev) UCL  ‐‐ ‐‐ 95% KM (t) UCL  ‐‐ ‐‐ 95% KM (t) UCL  Maximum Result  Maximum Result  Maximum Result  Maximum Result  99% KM (Chebyshev) UCL  97.5% KM (Chebyshev) UCL  ‐‐ Maximum Result  95% KM (t) UCL  97.5% KM (Chebyshev) UCL  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ Maximum Result  95% KM (t) UCL  ‐‐ ‐‐ 95% KM (t) UCL  ‐‐ Too Few Unique Detected Values  97.5% KM (Chebyshev) UCL  No Yes Yes No Yes No Yes Yes Yes No Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes No Yes No No No No No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes No No No Yes No Yes Yes No No Yes No Yes Yes Reason for Exclusionc Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background see  Xylenes, Total  Below Background PAGE 1 OF 3 TABLE E1‐1 Summary Statistics and Exposure Point Concentrations (EPCs) for Chemicals of Potential Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical  Pyrene   Selenium   Silver   Strontium   Styrene   Thallium   Vanadium   Xylenes, Total   Zinc   Zirconium  Soil 0‐10 ft bgs  1‐Methyl naphthalene   2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   2‐Methylnaphthalene   4,4'‐DDD   4,4'‐DDE   4,4'‐DDT   Acenaphthene   Acenaphthylene   Acetone   Aluminum   Anthracene   Antimony   Aroclor 1254   Aroclor 1260   Aroclor 5460   Arsenic   Barium   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   Beryllium   beta‐BHC   bis(2‐Ethylhexyl) phthalate   Boron   Butyl benzyl phthalate   Cadmium   Chromium   Chrysene   Cobalt   Copper   Dibenzo(a,h)anthracene   Diethyl phthalate   Di‐n‐butyl phthalate   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Ethylbenzene   Fluoranthene   Fluorene   Fluoride   Heptachlor   Heptachlor epoxide   Hexavalent Chromium  EN0317151003RDD Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Number of  Samples 31 40 43 4 17 40 40 19 40 37 Number of  Detects 13 27 35 4 6 35 40 1 40 36 Number of  Nondetects 18 13 8 0 11 5 0 18 0 1 Percent  Detected 42% 68% 81% 100% 35% 88% 100% 5% 100% 97% mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 58 40 16 58 22 22 22 58 58 35 71 58 76 35 35 3 92 75 58 58 58 58 54 71 22 58 69 58 76 72 58 71 72 58 58 58 58 22 22 22 22 35 58 58 38 22 22 29 3 38 2 4 2 6 10 2 3 1 71 12 30 20 3 1 88 75 22 20 28 16 12 69 1 2 35 6 74 72 34 71 72 4 1 5 3 1 1 1 2 1 26 2 24 1 1 15 55 2 14 54 20 16 12 56 55 34 0 46 46 15 32 2 4 0 36 38 30 42 42 2 21 56 34 52 2 0 24 0 0 54 57 53 55 21 21 21 20 34 32 56 14 21 21 14 5% 95% 13% 7% 9% 27% 45% 3% 5% 3% 100% 21% 39% 57% 9% 33% 96% 100% 38% 34% 48% 28% 22% 97% 5% 3% 51% 10% 97% 100% 59% 100% 100% 7% 2% 9% 5% 5% 5% 5% 9% 3% 45% 3% 63% 5% 5% 52% Minimum Non  Maximum  Detect Nondetect 0.0034 0.042 0.204 15 0.0522 2  NA   NA 0.0034 0.012 0.5 10  NA   NA 0.0034 0.012  NA   NA 1.56 1.56 0.0034 0.8 0.000000035 0.000000035 0.0107 0.05 0.0034 0.8 0.00284 0.034 0.00284 0.034 0.00284 0.004 0.0034 0.8 0.0034 0.8 0.00914 0.112  NA   NA 0.0034 0.8 0.149 20 0.0081 0.106 0.00712 0.106 0.0356 0.0406 10 12  NA   NA 0.0034 0.8 0.0034 0.044 0.0034 0.044 0.0034 0.044 0.0034 0.044 0.06 2 0.00142 0.02 0.0342 0.8 1.87 20 0.0342 0.48 0.8 2  NA   NA 0.0034 0.042  NA   NA  NA   NA 0.0034 0.044 0.0342 0.8 0.0342 0.8 0.0342 0.48 0.00142 0.0166 0.00284 0.034 0.00284 0.034 0.034 0.00284 0.00183 0.012 0.0034 0.8 0.0034 0.8 0.8 11.4 0.00142 0.0166 0.00142 0.0166 0.08 10 Minimum  Detect 0.00036 0.11 0.0297 18.2 0.000234 0.097 18 0.000372 15 0.78 Maximum  Detect 2.5 0.39 3.5 31.5 0.000723 0.419 58.9 0.000372 126 5.74  Mean Valuea 0.0846 0.196 0.196 NA  0.000406 0.269 41.3 NA  51.8 3.39 0.00089 4.35E‐10 0.018 0.00083 0.00035 0.0004 0.00053 0.00051 0.00048 0.016 4,440 0.00037 0.122 0.0047 0.00208 0.00706 0.73 49.1 0.0002 0.00023 0.00025 0.00025 0.00086 0.16 0.00073 0.0287 1.1 0.00059 0.035 6 0.00028 1.8 4.5 0.00093 0.00597 0.00096 0.0044 0.00055 0.00055 0.0005 0.00047 0.000312 0.00045 0.00089 0.2 0.00058 0.00047 0.22 0.0012 0.0000519 0.032 0.012 0.0018 0.0029 0.019 0.017 0.0021 0.016 33,200 0.13 7.5 0.099 0.046 0.00706 110 230 1.2 0.74 1 0.23 0.52 1.9 0.00073 0.0503 10.1 0.013 0.751 38.5 1.5 18.5 25.6 0.096 0.00597 0.0023 0.099 0.00055 0.00055 0.0005 0.0011 0.000312 2.3 0.015 11.2 0.00058 0.00047 3.2 0.00101 0.00000656 0.0164 0.00144 0.00108 0.00136 0.00266 0.000912 0.00113 NA  17,600 0.0031 0.352 0.0238 0.00562 NA  12.8 110 0.0225 0.0144 0.0201 0.00565 0.0111 0.786 NA  0.0291 3.57 0.00325 0.184 22.6 0.0289 6.72 12.1 0.00303 NA  0.00141 0.00874 NA  NA  NA  0.000785 NA  0.0434 0.00123 2.1 NA  NA  0.696  Standard Deviationa 0.441 0.0749 0.549 NA  0.000181 0.0794 8.59 NA  18.8 1.24 Exposure Point Concentrationb 0.905 ‐‐ 0.569 ‐‐ 0.000548 ‐‐ ‐‐ 0.000372 ‐‐ ‐‐ 0.000136 0.0000115 0.00829 0.00169 0.000725 0.000838 0.00397 0.00254 0.000701 NA  5,840 0.017 0.855 0.0257 0.00813 NA  17.8 28.5 0.156 0.0961 0.13 0.0298 0.0699 0.274 NA  0.00297 2.7 0.00441 0.126 6.59 0.195 2.49 4.16 0.0124 NA  0.00047 0.0128 NA  NA  NA  0.000315 NA  0.299 0.00218 2.31 NA  NA  0.687 ‐‐ 0.0000249 0.0256 0.00203 0.0018 ‐‐ 0.00423 0.0065 0.00195 0.016 ‐‐ 0.0133 0.52 0.0319 0.0103 0.00706 16.5 ‐‐ 0.114 0.0708 0.0958 0.0233 0.0544 ‐‐ 0.00073 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.191 ‐‐ ‐‐ 0.00619 ‐‐ ‐‐ 0.0138 0.00055 0.00055 0.0005 0.0011 0.000312 0.218 0.00333 2.81 0.00058 0.00047 0.932 EPC Basis 99% KM (Chebyshev) UCL  ‐‐ 95% KM (Chebyshev) UCL  ‐‐ 95% KM (t) UCL  ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ 99% KM (Chebyshev) UCL  95% KM (t) UCL  95% KM (t) UCL  Maximum Result  ‐‐ 95% KM (t) UCL  99% KM (Chebyshev) UCL  95% KM (t) UCL  Maximum Result  ‐‐ 95% KM (Chebyshev) UCL  95% KM (t) UCL  95% KM (t) UCL  95% KM (t) UCL  Maximum Result  95% KM (BCA) UCL  ‐‐ 95% KM (Chebyshev) UCL  95% KM (Chebyshev) UCL  95% KM (Chebyshev) UCL  95% KM (Chebyshev) UCL  95% KM (Chebyshev) UCL  ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 97.5% KM (Chebyshev) UCL  ‐‐ ‐‐ 95% KM (t) UCL  ‐‐ ‐‐ 95% KM (t) UCL  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  95% KM (Chebyshev) UCL  95% KM (Chebyshev) UCL  95% KM (BCA) UCL  Maximum Result  Maximum Result  95% KM (t) UCL  COPC Yes No Yes No Yes No No Yes No No No Yes Yes Yes Yes No Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes No Yes No No No No No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Reason for Exclusionc Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background PAGE 2 OF 3 TABLE E1‐1 Summary Statistics and Exposure Point Concentrations (EPCs) for Chemicals of Potential Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical  Indeno(1,2,3‐cd)pyrene   Lead   Lithium   Manganese   MCPA   Mercury   Methylene chloride   Mirex   Molybdenum   m‐Xylene & p‐Xylene   Naphthalene   Nickel   Perchlorate   Phenanthrene   Pyrene   Selenium   Silver   Silvex   Strontium   Styrene   Thallium   Tin   Vanadium   Xylenes, Total   Zinc   Zirconium  Soil Vapor  1,1,1‐Trichloroethane   1,1,2‐Trichloro‐1,2,2‐trifluoroethane   Benzene   Chloroform   Dichlorodifluoromethane   Ethylbenzene   o‐Xylene   Tetrachloroethene   Toluene   Trichloroethene   Trichlorofluoromethane   Xylenes, Total  Notes: a Units mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Number of  Samples 58 71 68 45 16 40 35 22 71 34 58 71 19 58 58 71 74 16 6 32 71 6 71 35 71 68 Number of  Detects 9 69 68 45 1 27 2 4 63 2 13 71 4 24 23 36 62 1 6 11 65 1 71 2 71 64 Number of  Nondetects 49 2 0 0 15 13 33 18 8 32 45 0 15 34 35 35 12 15 0 21 6 5 0 33 0 4 Percent  Detected 16% 97% 100% 100% 6% 68% 6% 18% 89% 6% 22% 100% 21% 41% 40% 51% 84% 6% 100% 34% 92% 17% 100% 6% 100% 94% µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L 26 26 26 26 26 26 26 26 26 26 26 26 2 3 1 1 1 3 4 1 4 3 2 5 24 23 25 25 25 23 22 25 22 23 24 21 8% 12% 4% 4% 4% 12% 15% 4% 15% 12% 8% 19% Minimum Non  Maximum  Detect Nondetect 0.0034 0.8 8.4 10  NA   NA  NA   NA 2.14 5.6 0.0114 0.4 0.004 0.044 0.00142 0.004 0.214 20 0.0034 0.012 0.0034 0.8  NA   NA 0.00434 0.012 0.0034 0.8 0.0034 0.042 0.204 15 0.0438 2 0.0034 0.0044  NA   NA 0.0034 0.012 0.46 10 0.564 7.32  NA   NA 0.0034 0.012  NA   NA 1.5 2.8 0.04 0.2 0.0064 0.04 0.04 0.2 0.04 0.04 0.046 0.0108 0.2 0.2 2 2 2 2 2 2 2 2 2 2 2 4 Minimum  Detect 0.00093 1.8 8.5 158 0.94 0.0025 0.0027 0.0004 0.14 0.000372 0.00042 3 0.0039 0.00049 0.00024 0.11 0.0297 0.0014 18.2 0.000234 0.097 0.384 18 0.000372 15 0.78 Maximum  Detect 0.26 16.5 58 887 0.94 0.033 0.00281 0.0047 0.961 0.00136 0.0022 32.2 0.043 0.91 2.5 0.76 3.5 0.0014 41.3 0.000723 0.427 0.384 73 0.00136 126 8.19  Mean Valuea 0.00612 7.9 25 340 NA  0.0101 0.00276 0.001 0.4 0.000866 0.00126 16.4 0.00731 0.0182 0.0465 0.21 0.155 NA  27.4 0.000431 0.272 NA  42.5 0.000866 52.6 3.52 0.0016 0.02 0.13 0.0021 0.0014 0.0025 0.0027 0.0095 0.00089 9.2 0.02 0.0085 1.5 1.5 0.13 0.0021 0.0014 0.12 0.11 0.0095 0.95 120 0.022 0.54 0.0667 0.107 NA  NA  NA  0.0455 0.0491 NA  0.0961 5.4 0.021 0.0725  Standard Deviationa 0.0339 2.74 10.1 135 NA  0.00625 0.000055 0.000884 0.179 0.000494 0.000453 6.05 0.00951 0.118 0.325 0.111 0.423 NA  8.02 0.000167 0.0773 NA  9.2 0.000494 17.2 1.47 Exposure Point Concentrationb 0.0269 ‐‐ ‐‐ ‐‐ 0.94 ‐‐ 0.00281 0.00153 ‐‐ ‐‐ 0.00148 ‐‐ 0.0117 0.0488 0.237 ‐‐ 0.254 0.0014 ‐‐ 0.000521 ‐‐ ‐‐ ‐‐ 0.00136 ‐‐ ‐‐ EPC Basis 95% KM (Chebyshev) UCL  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ Maximum Result  95% KM (t) UCL  ‐‐ ‐‐ 95% KM (t) UCL  ‐‐ 95% KM (t) UCL  95% KM (BCA) UCL  95% KM (Chebyshev) UCL  ‐‐ 95% KM (BCA) UCL  Maximum Result  ‐‐ 95% KM (t) UCL  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ COPC Yes No No No Yes No Yes Yes No No Yes No Yes Yes Yes No Yes Yes No Yes No No No Yes No No 0.306 0.305 NA  NA  NA  0.0529 0.0424 NA  0.198 23.1 0.001 0.125 0.963 0.245 0.13 0.0021 0.0014 0.109 ‐‐ 0.0095 0.198 14.9 0.022 0.128 99% KM (Chebyshev) UCL  95% KM (t) UCL  Maximum Result  Maximum Result  Maximum Result  95% KM (t) UCL  ‐‐ Maximum Result  95% KM (t) UCL  95% KM (t) UCL  Maximum Result  95% KM (t) UCL  Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Reason for Exclusionc Below Background Below Background Below Background Below Background Below Background see  Xylenes, Total  Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background see  Xylenes, Total   Kaplan Meier statistics are provided in these columns when nondetects are present. b  When more than one recommended UCL was given, the highest was selected as the EPC. If the recommended UCL exceeded the maximum detect, the maximum detect was selected as the EPC.  Background comparisons provided in Tables 2 and 3 of Attachment 1. µg/L = micrograms per liter bgs = below ground surface COPC = chemical of potential concern EPC = exposure point concentration KM = Kaplan Meier mg/kg = milligrams per kilogram NA = insufficient number of detected values, UCL could not be calculated TEQ = 2,3,7,8‐TCDD toxicity equivalents UCL = upper confidence limit on the mean c EN0317151003RDD PAGE 3 OF 3 TABLE E1‐2 Summary Statistics and Exposure Point Concentrations (EPCs) for Radionuclides of Potential Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Soil 0‐2 ft bgs  Actinium‐228   Americium‐241   Americium‐243   Antimony‐125   Barium‐137m   Bismuth‐212   Bismuth‐214   Cesium‐134   Cesium‐137   Curium‐243/244   Europium‐155   Lead‐212   Lead‐214   Plutonium‐239/240   Plutonium‐244   Potassium‐40   Radon‐220   Radon‐222   Strontium‐90   Tellurium‐125m   Thallium‐208   Thorium‐228   Thorium‐229   Thorium‐230   Thorium‐232   Thorium‐234   Uranium‐233/234   Uranium‐235/236   Uranium‐238   Yttrium‐90  Soil 0‐10 ft bgs  Actinium‐228   Americium‐241   Americium‐243   Antimony‐125   Barium‐137m   Bismuth‐212   Bismuth‐214   Cesium‐134   Cesium‐137   Curium‐243/244   Europium‐155   Lead‐212   Lead‐214   Plutonium‐239/240   Plutonium‐244   Potassium‐40   Radon‐220   Radon‐222   Strontium‐90   Tellurium‐125m   Thallium‐208   Thorium‐228   Thorium‐229   Thorium‐230  EN0317151003RDD Exposure Standard  Point Deviation of  Detects Concentrationb Units Number of  Samples Number of  Detects Number of  Nondetects Percent  Detected Minimum  Nondetecta Maximum  Nondetecta Minimum  Detect Maximum  Detect Mean of  Detects  pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g  5 5 4 5 1 5 5 5 5 5 5 5 5 5 1 5 1 1 5 1 5 5 5 5 5 5 5 5 5 4 5 4 2 2 1 5 5 1 5 2 5 5 5 2 1 5 1 1 1 1 5 5 2 5 5 5 5 5 5 1 0 1 2 3 0 0 0 4 0 3 0 0 0 3 0 0 0 0 4 0 0 0 3 0 0 0 0 0 0 3 100% 80% 50% 40% 100% 100% 100% 20% 100% 40% 100% 100% 100% 40% 100% 100% 100% 100% 20% 100% 100% 100% 40% 100% 100% 100% 100% 100% 100% 25% NA  0.0087 0.0215 0.0366 NA  NA  NA  0.0122 NA  0.0025 NA  NA  NA  0.0015 NA  NA  NA  NA  0.054 NA  NA  NA  0.021 NA  NA  NA  NA  NA  NA  0.177 NA 0.0087 0.0226 0.04 NA NA NA 0.058 NA 0.0209 NA NA NA 0.0185 NA NA NA NA 0.314 NA NA NA 0.0962 NA NA NA NA NA NA 0.314 0.993 0.00175 0.00703 0.025 0.0267 0.693 0.856 0.0109 0.0166 0.00182 0.0511 1.2 0.948 0.00409 0.0022 18.6 1.37 1 0.275 0.0276 0.364 0.761 0.0376 0.599 0.76 1.02 0.48 0.0252 0.518 0.275 1.32 0.0135 0.0129 0.119 0.0267 1.1 0.99 0.0109 0.0446 0.0128 0.089 1.64 1.06 0.00783 0.0022 20.1 1.37 1 0.275 0.0276 0.545 1.25 0.0454 0.958 1.23 1.76 0.852 0.0564 0.837 0.275 1.11 0.00608  NA  0.0438  NA  0.842 0.897  NA  0.0327 0.00548 0.0719 1.32 0.997 0.00447  NA  19.3  NA   NA   NA   NA  0.408 1.1 0.0347 0.777 1.06 1.41 0.651 0.0429 0.662  NA  0.123 0.00403 NA  0.0376 NA  0.155 0.0567 NA  0.0107 0.00518 0.0142 0.189 0.0458 0.0026 NA  0.607 NA  NA  NA  NA  0.0771 0.203 0.0102 0.145 0.189 0.27 0.134 0.0127 0.145 NA  ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0022 ‐‐ ‐‐ ‐‐ 0.275 ‐‐ ‐‐ ‐‐ 0.0454 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.275 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Maximum Result  No No No No No No No No No No No No No No Yes No No No Yes No No No Yes No No No No No No Yes  pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g   pCi/g  5 5 4 5 1 5 5 5 5 5 5 5 5 5 1 5 1 1 5 1 5 5 5 5 5 4 2 2 1 5 5 1 5 2 5 5 5 2 1 5 1 1 1 1 5 5 2 5 0 1 2 3 0 0 0 4 0 3 0 0 0 3 0 0 0 0 4 0 0 0 3 0 100% 80% 50% 40% 100% 100% 100% 20% 100% 40% 100% 100% 100% 40% 100% 100% 100% 100% 20% 100% 100% 100% 40% 100% NA  0.0087 0.0215 0.0366 NA  NA  NA  0.0122 NA  0.0025 NA  NA  NA  0.0015 NA  NA  NA  NA  0.054 NA  NA  NA  0.021 NA  NA 0.0087 0.0226 0.04 NA NA NA 0.058 NA 0.0209 NA NA NA 0.0185 NA NA NA NA 0.314 NA NA NA 0.0962 NA 0.993 0.00175 0.00703 0.025 0.0267 0.693 0.856 0.0109 0.0166 0.00182 0.0511 1.2 0.948 0.00409 0.0022 18.6 1.37 1 0.275 0.0276 0.364 0.761 0.0376 0.599 1.32 0.0135 0.0129 0.119 0.0267 1.1 0.99 0.0109 0.0446 0.0128 0.089 1.64 1.06 0.00783 0.0022 20.1 1.37 1 0.275 0.0276 0.545 1.25 0.0454 0.958 1.11 0.00608  NA  0.0438  NA  0.842 0.897  NA  0.0327 0.00548 0.0719 1.32 0.997 0.00447  NA  19.3  NA   NA   NA   NA  0.408 1.1 0.0347 0.777 0.123 0.00403 NA  0.0376 NA  0.155 0.0567 NA  0.0107 0.00518 0.0142 0.189 0.0458 0.0026 NA  0.607 NA  NA  NA  NA  0.0771 0.203 0.0102 0.145 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0022 ‐‐ ‐‐ ‐‐ 0.275 ‐‐ ‐‐ ‐‐ 0.0454 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ ‐‐ ‐‐ Maximum Result  ‐‐ No No No No No No No No No No No No No No Yes No No No Yes No No No Yes No EPC Basis ROPC Reason for Exclusionc Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background Below Background PAGE 1 OF 2 TABLE E1‐2 Summary Statistics and Exposure Point Concentrations (EPCs) for Radionuclides of Potential Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California EN0317151003RDD Number of  Detects 5 5 5 5 5 1 Number of  Nondetects 0 0 0 0 0 3 Percent  Detected 100% 100% 100% 100% 100% 25% Minimum  Nondetecta NA  NA  NA  NA  NA  0.177 Exposure Standard  Point Deviation of  Detects Concentrationb 0.189 ‐‐ 0.27 ‐‐ 0.134 ‐‐ 0.0127 ‐‐ 0.145 ‐‐ NA  0.275 Reason for Chemical Units EPC Basis ROPC Exclusionc  Thorium‐232   pCi/g  ‐‐ No Below Background  Thorium‐234   pCi/g  ‐‐ No Below Background  Uranium‐233/234   pCi/g  ‐‐ No Below Background  Uranium‐235/236   pCi/g  ‐‐ No Below Background  Uranium‐238   pCi/g  ‐‐ No Below Background  Yttrium‐90   pCi/g  Maximum Result  Yes Notes: a  The minimum detectable concentration (MDC) was used for all non‐detect results.   b  When more than one recommended UCL was given the highest was selected as the EPC. If the recommended UCL exceeded the maximum detect the maximum detect was selected as the EPC c  UTL 95‐95 BTV ‐ for combined strata as presented in Table 5 SSFL Chemical Soil Background Study, Chemical Analytes ‐ Summary of Statistical Evaluation Results as published in DTSC's Final Chemical Background Study Report (Dec 2012); and, DTSC table  'Background Threshold Values Using Combined Chemical Background Data' as published in 'Combined‐Data Background Thresholds Values and Methodology Narrative' (Dec 2012). If a BTV was not assigned by DTSC, the maximum reported RL in the background  dataset was used.  bgs = below ground surface BTV = background threshold value EPC = exposure point concentration KM = Kaplan Meier mg/kg = milligrams per kilogram NA = insufficient number of detected values, UCL could not be calculated pCi/g ‐ picocuries per gram ROPC = radionuclide of potential concern SSFL = Santa Susanna Field Laboratory UCL = upper confidence limit on the mean UTL = upper threshold limit Number of  Samples 5 5 5 5 5 4 Maximum  Nondetecta NA NA NA NA NA 0.314 Minimum  Detect 0.76 1.02 0.48 0.0252 0.518 0.275 Maximum  Detect 1.23 1.76 0.852 0.0564 0.837 0.275 Mean of  Detects 1.06 1.41 0.651 0.0429 0.662  NA  PAGE 2 OF 2 TABLE E1‐3 Chemical Risk Summary by Exposure Scenario RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Exposure Scenario Suburban Residential Scenario Site Soil 0 to 2 ft bgs Direct Contact Site Soil 0 to 10 ft bgs Direct Contact b Background Soil Direct Contact Incremental Risk for Soil Contactc Soil Vapor (Indoor Air Pathway) Groundwater (Domestic use of well HAR‐18) Noncancer Hazard Index 4E‐04 2 3E‐04 1 2E‐04 3E‐04 3E‐05 0.5 2 7 3E‐02 426 3E‐02 320 1E‐04 0.4 4E‐05 7E‐05 7E‐05 0.1 0.3 0.3 d Multimedia Riske Recreational Scenario Site Soil 0 to 2 ft bgs Direct Contact Background Soil Direct Contact Excess Lifetime Cancer Risk b Incremental Risk for Soil Contactc Multimedia Riskf Primary Contributors to Cancer Riska Primary Contributors to Hazard Indexa Arsenic (ELCR=4E‐4, 97%) Benzo[a]pyrene (ELCR=5E‐6, 1%) 2,3,7,8‐TCDD TEQ (ELCR=4E‐6, 1%) Arsenic (ELCR=3E‐4, 97%) 2,3,7,8‐TCDD TEQ (ELCR=5E‐6, 2%) Benzo(a)pyrene (ELCR=2E‐6, <1%) Arsenic (ELCR=2E‐4, >99%) Arsenic (HQ=1, 67%) Trichloroethene (ELCR=3E‐5, 94%) Benzene (ELCR=2E‐6, 6%) Vinyl chloride (ELCR=3E‐02, 87%) n‐Nitrosodimethylamine (ELCR=2E‐03, 8%) Trichloroethene (ELCR=2E‐03, 5%) 1,1‐Dichloropropene (ELCR=3E‐05, <1%) Heptachlor (ELCR=2E‐05, <1%) 1,4‐Dioxane (ELCR=6E‐06, <1%) gamma‐BHC (ELCR=4E‐06, <1%) Aldrin (ELCR=3E‐06, <1%) 1 1‐Dichloroethane (ELCR=2E‐06 <1%) Trichloroethene (HQ=7, >99%) Arsenic (ELCR=1E‐4, 96%) Benzo(a)pyrene (ELCR=2E‐6, 2%) Arsenic (ELCR=4E‐5, >99%) None identified None identified Trichloroethene (HQ=230, 54%) cis‐1,2‐Dichloroethene (HQ=163, 38%) n‐Nitrosodimethylamine (HQ=23, 5%) Vinyl chloride (HQ=8, 2%) None identified None identified Notes: a ‐6  Primary contributors to the total risk are listed when chemical‐specific risk > 10 . Primary contributors to the hazard index (HI) are listed when HI > 1.   Background risk is based on data from the Final Chemical Soil Background Study Report (DTSC, 2012). c  Incremental risk is calculated as the site risk minus the background risk. For the suburban resident, the higher risk of 0 to 2 ft bgs or 0 to 10 ft bgs is used in the calculation. d  The highest risk well point within Boeing RFI Subarea 5/9 South is listed. e  Includes risks from combined exposure from 1) direct contact with soil, 2) inhalation of indoor air vapors originating from soil vapor, and 3) domestic use of shallow groundwater.  f  Includes risks from exposure from direct contact with soil only. There are no sediment or surface water data or risk estimates. bgs = below ground surface ELCR = excess lifetime cancer risk ft = feet HQ = hazard quotient TEQ = 2,3,7,8‐TCDD toxicity equivalents b EN0317151003RDD PAGE 1 OF 1 TABLE E1‐4 Radiological Risk Summary by Exposure Scenario RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Exposure Scenario Suburban Residential Scenario Site Soil 0 to 2 ft bgs Direct Contact Background Soil Direct Contact b Incremental Risk for Soil Contactc Shallow Groundwater (Domestic use) d e Multi‐Media Risk Recreational Scenario Site Soil 0 to 2 ft bgs Direct Contact Background Soil Direct Contact b Incremental Risk for Soil Contactc Multi‐Media Riskf Excess Lifetime Cancer Risk Primary Contributors to Cancer Riska 2E‐07 NA 2E‐07 2E‐05 2E‐05 None identified NA 4E‐08 NA 4E‐08 4E‐08 Uranium‐233/234, Dissolved (ELCR=1E‐5, 94%) None identified NA Notes: a ‐6  Primary contributors to the total risk are listed when chemical‐specific risk > 10 . b  Background risk is based on data from the Final Chemical Soil Background Study Report (DTSC, 2012). c  Incremental risk is calculated as the site risk minus the background risk.  d  The highest risk well point within Boeing RFI Subarea 5/9 South is listed. e  Includes risks from combined exposure from 1) direct contact/external exposure with soil, and 2) domestic use of shallow groundwater.  f  Includes risks from exposure from direct contact with soil only. There are no sediment or surface water data or risk estimates. bgs = below ground surface ELCR = excess lifetime cancer risk ft = feet NA = background exposure point concentrations not computed for the radionuclides of potential concern EN0317151003RDD PAGE 1 OF 1 TABLE E1‐5 Risk and Hazard Estimates for Exposure to Soil (0 to 2 feet bgs)  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analyte  2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   4,4'‐DDD   4,4'‐DDT   Acenaphthene   Acenaphthylene   Anthracene   Antimony   Aroclor 1254   Aroclor 1260   Arsenic   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   beta‐BHC   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Fluoranthene   Fluorene   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   MCPA   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Styrene   Xylenes, Total  Exposure Point  Concentration (mg/kg) 2.10E‐05 3.20E‐02 1.80E‐03 6.37E‐03 1.11E‐02 1.97E‐03 5.07E‐02 7.91E‐01 4.73E‐02 3.79E‐02 2.64E+01 4.34E‐01 1.79E‐01 3.60E‐01 5.68E‐02 2.19E‐01 7.30E‐04 5.38E‐01 1.05E‐02 1.76E‐02 5.50E‐04 5.50E‐04 5.00E‐04 1.10E‐03 8.31E‐01 6.80E‐03 4.70E‐04 1.13E+00 6.75E‐02 9.40E‐01 2.70E‐03 1.84E‐03 1.61E‐03 1.50E‐02 2.19E‐01 9.05E‐01 5.69E‐01 5.48E‐04 3.72E‐04 Carcinogenic RBSLa (mg/kg) 4.81E‐06 ‐‐ 2.46E+00 1.74E+00 ‐‐ ‐‐ ‐‐ ‐‐ 2.32E‐01 2.32E‐01 6.58E‐02 3.87E‐01 3.87E‐02 3.87E‐01 ‐‐ 3.87E‐01 3.94E‐01 3.87E+00 1.13E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.07E‐01 1.29E+00 3.87E‐01 ‐‐ 2.97E+00 3.28E‐02 1.46E+01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Soil Contact Exposure Scenario Noncarcinogenic Cancer Percent RBSLa Hazard Risk Contribution (mg/kg) Quotient 4.37E‐06 1.1% 5.05E‐05 4.16E‐01 ‐‐ ‐‐ 5.49E+02 5.83E‐05 7.31E‐10 0.0% ‐‐ ‐‐ 3.66E‐09 0.0% 3.43E+01 1.86E‐04 ‐‐ ‐‐ 3.23E+03 3.44E‐06 ‐‐ ‐‐ 2.98E+03 6.62E‐07 ‐‐ ‐‐ 1.64E+04 3.09E‐06 ‐‐ ‐‐ 2.64E+01 3.00E‐02 2.04E‐07 0.0% 1.10E+00 4.29E‐02 1.63E‐07 0.0% 1.10E+00 3.44E‐02 4.01E‐04 96.8% 2.16E+01 1.22E+00 1.12E‐06 0.3% ‐‐ ‐‐ 4.62E‐06 1.1% ‐‐ ‐‐ 9.30E‐07 0.2% ‐‐ ‐‐ ‐‐ ‐‐ 1.65E+03 3.44E‐05 5.66E‐07 0.1% ‐‐ ‐‐ 1.85E‐09 0.0% ‐‐ ‐‐ 1.39E‐07 0.0% ‐‐ ‐‐ 9.27E‐08 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 6.11E+02 2.88E‐05 ‐‐ ‐‐ 4.12E+02 1.34E‐06 ‐‐ ‐‐ 4.12E+02 1.34E‐06 ‐‐ ‐‐ 2.06E+01 2.43E‐05 ‐‐ ‐‐ 2.06E+01 5.34E‐05 ‐‐ ‐‐ 2.20E+03 3.77E‐04 ‐‐ ‐‐ 2.18E+03 3.12E‐06 4.37E‐09 0.0% 8.92E‐01 5.27E‐04 8.73E‐07 0.2% 2.34E+02 4.82E‐03 1.74E‐07 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 3.43E+01 2.74E‐02 9.08E‐10 0.0% 2.90E+02 9.31E‐06 5.60E‐08 0.0% 1.37E+01 1.34E‐04 1.10E‐10 0.0% 6.81E+02 2.36E‐06 ‐‐ ‐‐ 5.33E+01 2.82E‐04 ‐‐ ‐‐ 1.64E+04 1.33E‐05 ‐‐ ‐‐ 1.65E+03 5.48E‐04 ‐‐ ‐‐ 2.30E+02 2.47E‐03 ‐‐ ‐‐ 1.14E+04 4.82E‐08 ‐‐ ‐‐ 4.28E+02 8.69E‐07 4E‐04 100.0% Hazard Index 2 Percent Contribution 23.3% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% 1.7% 2.4% 1.9% 68.6% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.3% ‐‐ 1.5% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.1% 0.0% 0.0% 100.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Carcinogenic RBSLa (mg/kg) 7.51E‐09 ‐‐ 4.04E‐03 2.87E‐03 ‐‐ ‐‐ ‐‐ ‐‐ 4.88E‐04 4.89E‐04 9.92E‐05 8.05E‐04 8.09E‐05 8.05E‐04 ‐‐ 8.09E‐04 5.48E‐04 8.06E‐03 2.38E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.71E‐04 1.94E‐03 8.13E‐04 ‐‐ 1.06E‐02 5.42E‐05 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Garden Exposure Scenario Noncarcinogenic Cancer Percent RBSLa Hazard Risk Contribution (mg/kg) Quotient 2.80E‐03 1.0% 2.52E‐07 8.32E+01 ‐‐ ‐‐ 2.29E+00 1.40E‐02 4.45E‐07 0.0% ‐‐ ‐‐ 2.22E‐06 0.0% 1.80E‐01 3.53E‐02 ‐‐ ‐‐ 1.87E+01 5.92E‐04 ‐‐ ‐‐ 1.88E+01 1.05E‐04 ‐‐ ‐‐ 1.01E+02 5.04E‐04 ‐‐ ‐‐ 1.39E‐01 5.68E+00 9.70E‐05 0.0% 7.21E‐03 6.56E+00 7.75E‐05 0.0% 7.23E‐03 5.24E+00 2.66E‐01 97.3% 1.04E‐01 2.53E+02 5.39E‐04 0.2% ‐‐ ‐‐ 2.21E‐03 0.8% ‐‐ ‐‐ 4.47E‐04 0.2% ‐‐ ‐‐ ‐‐ ‐‐ 1.08E+01 5.26E‐03 2.71E‐04 0.1% ‐‐ ‐‐ 1.33E‐06 0.0% ‐‐ ‐‐ 6.68E‐05 0.0% ‐‐ ‐‐ 4.41E‐05 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 3.61E+00 4.87E‐03 ‐‐ ‐‐ 1.84E+00 2.98E‐04 ‐‐ ‐‐ 1.77E+00 3.10E‐04 ‐‐ ‐‐ 1.05E‐01 4.74E‐03 ‐‐ ‐‐ 1.03E‐01 1.06E‐02 ‐‐ ‐‐ 1.40E+01 5.92E‐02 ‐‐ ‐‐ 1.30E+01 5.22E‐04 2.74E‐06 0.0% 4.53E‐03 1.04E‐01 5.81E‐04 0.2% 1.08E+00 1.05E+00 8.31E‐05 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 1.31E‐01 7.20E+00 2.54E‐07 0.0% 3.30E‐01 8.18E‐03 3.39E‐05 0.0% 7.21E‐02 2.55E‐02 ‐‐ ‐‐ 5.31E+00 3.03E‐04 ‐‐ ‐‐ 1.58E‐02 9.48E‐01 ‐‐ ‐‐ 1.01E+02 2.17E‐03 ‐‐ ‐‐ 1.04E+01 8.71E‐02 ‐‐ ‐‐ 1.81E+00 3.15E‐01 ‐‐ ‐‐ 4.59E+01 1.19E‐05 ‐‐ ‐‐ 4.96E+01 7.50E‐06 3E‐01 100.0% Hazard Index 363 Extrapolated PCB Congeners PCB TEQ 6.23E‐05 3.57E‐06 2E‐05 100.0% 3.86E‐05 2 100.0% 7.50E‐09 8E‐03 100.0% Notes: a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory, Ventura County California (MWH, 2014). bgs = below ground surface mg/kg = milligrams per kilogram PCB = polychlorinated biphenyl TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0317151003RDD 2.52E‐07 247 Percent Contribution 22.9% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% 1.6% 1.8% 1.4% 69.6% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.3% ‐‐ 2.0% 0.0% 0.0% 0.0% 0.3% 0.0% 0.0% 0.1% 0.0% 0.0% 100.0% 100.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Carcinogenic RBSLa (mg/kg) 1.80E‐05 ‐‐ 8.26E+00 5.83E+00 ‐‐ ‐‐ ‐‐ ‐‐ 5.64E‐01 5.64E‐01 2.46E‐01 9.39E‐01 9.39E‐02 9.39E‐01 ‐‐ 9.39E‐01 1.32E+00 9.39E+00 2.75E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.60E‐01 6.27E+00 9.39E‐01 ‐‐ 3.71E+01 1.10E‐01 2.04E+02 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Cancer Risk 1.17E‐06 ‐‐ 2.18E‐10 1.09E‐09 ‐‐ ‐‐ ‐‐ ‐‐ 8.39E‐08 6.72E‐08 1.07E‐04 4.62E‐07 1.91E‐06 3.83E‐07 ‐‐ 2.33E‐07 5.52E‐10 5.73E‐08 3.82E‐08 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.30E‐09 1.80E‐07 7.19E‐08 ‐‐ 7.28E‐11 1.67E‐08 7.89E‐12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1E‐04 8.67E‐06 7E‐06 Recreational Exposure Scenario Noncarcinogenic Percent RBSLa Contribution (mg/kg) 1.0% 2.36E‐04 ‐‐ 2.56E+03 0.0% ‐‐ 0.0% 1.60E+02 ‐‐ 1.53E+04 ‐‐ 1.49E+04 ‐‐ 7.70E+04 ‐‐ 1.23E+02 0.1% 5.14E+00 0.1% 5.14E+00 95.8% 1.01E+02 0.4% ‐‐ 1.7% ‐‐ 0.3% ‐‐ ‐‐ 7.71E+03 0.2% ‐‐ 0.0% ‐‐ 0.1% ‐‐ 0.0% ‐‐ ‐‐ 2.85E+03 ‐‐ 1.92E+03 ‐‐ 1.92E+03 ‐‐ 9.61E+01 ‐‐ 9.61E+01 ‐‐ 1.03E+04 ‐‐ 1.02E+04 0.0% 4.16E+00 0.2% 1.09E+03 0.1% ‐‐ ‐‐ 1.60E+02 0.0% 1.82E+03 0.0% 6.40E+01 0.0% 4.26E+03 ‐‐ 2.49E+02 ‐‐ 7.70E+04 ‐‐ 7.71E+03 ‐‐ 1.07E+03 ‐‐ 6.49E+04 ‐‐ 5.69E+03 100.0% Hazard Index 100.0% 1.80E‐04 Hazard Quotient 8.91E‐02 1.25E‐05 ‐‐ 3.98E‐05 7.26E‐07 1.32E‐07 6.59E‐07 6.43E‐03 9.20E‐03 7.37E‐03 2.61E‐01 ‐‐ ‐‐ ‐‐ 7.37E‐06 ‐‐ ‐‐ ‐‐ ‐‐ 6.17E‐06 2.86E‐07 2.86E‐07 5.21E‐06 1.15E‐05 8.08E‐05 6.64E‐07 1.13E‐04 1.03E‐03 ‐‐ 5.87E‐03 1.49E‐06 2.87E‐05 3.78E‐07 6.04E‐05 2.85E‐06 1.17E‐04 5.30E‐04 8.44E‐09 6.54E‐08 0.4 Percent Contribution 23.4% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% 1.7% 2.4% 1.9% 68.5% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.3% ‐‐ 1.5% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.1% 0.0% 0.0% 100.0% 0.3 100.0% PAGE 1 OF 1 TABLE E1‐6 Risk and Hazard Estimates for Exposure to Background Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analyte 2,3,7,8‐TCDD TEQ 2,4‐Dichlorophenoxybutyric acid 4,4'‐DDD 4,4'‐DDT Acenaphthylene Anthracene Antimony Arsenic Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene beta‐BHC Chrysene Dibenzo(a,h)anthracene Di‐n‐octyl phthalate Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Fluoranthene Fluorene Heptachlor epoxide Hexavalent Chromium Indeno(1,2,3‐cd)pyrene MCPA Mirex Naphthalene Perchlorate Phenanthrene Pyrene Silver Exposure Point  Concentration (mg/kg) 2.78E‐07 1.92E‐03 9.35E‐05 2.48E‐03 4.04E‐04 3.72E‐04 2.56E‐01 1.08E+01 7.61E‐04 8.47E‐04 1.43E‐03 7.54E‐04 1.40E‐03 7.20E‐05 1.17E‐03 7.16E‐04 6.04E‐03 5.17E‐05 8.77E‐05 8.72E‐05 1.58E‐04 1.30E‐03 8.83E‐04 5.51E‐05 5.53E‐01 6.85E‐04 1.42E‐01 1.36E‐04 8.61E‐04 3.87E‐04 9.44E‐04 1.21E‐03 5.20E‐02 Carcinogenic RBSLa (mg/kg) 4.81E‐06 ‐‐ 2.46E+00 1.74E+00 ‐‐ ‐‐ ‐‐ 6.58E‐02 3.87E‐01 3.87E‐02 3.87E‐01 ‐‐ 3.87E‐01 3.94E‐01 3.87E+00 1.13E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.07E‐01 1.29E+00 3.87E‐01 ‐‐ 3.28E‐02 1.46E+01 ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Soil Contact Exposure Scenario Noncarcinogenic Cancer Risk 5.77E‐08 ‐‐ 3.80E‐11 1.43E‐09 ‐‐ ‐‐ ‐‐ 1.65E‐04 1.97E‐09 2.19E‐08 3.69E‐09 ‐‐ 3.62E‐09 1.83E‐10 3.02E‐10 6.32E‐09 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 5.13E‐10 4.27E‐07 1.77E‐09 ‐‐ 4.14E‐09 5.91E‐11 ‐‐ ‐‐ ‐‐ ‐‐ 2E‐04 Percent Contribution 0.0% ‐‐ 0.0% 0.0% ‐‐ ‐‐ ‐‐ 99.7% 0.0% 0.0% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.3% 0.0% ‐‐ 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 100.0% RBSLa (mg/kg) 5.05E‐05 5.49E+02 ‐‐ 3.43E+01 2.98E+03 1.64E+04 2.64E+01 2.16E+01 ‐‐ ‐‐ ‐‐ 1.65E+03 ‐‐ ‐‐ ‐‐ ‐‐ 6.11E+02 4.12E+02 4.12E+02 2.06E+01 2.06E+01 2.20E+03 2.18E+03 8.92E‐01 2.34E+02 ‐‐ 3.43E+01 1.37E+01 6.81E+02 5.33E+01 1.64E+04 1.65E+03 2.30E+02 Hazard Index Hazard Quotient 5.50E‐03 3.50E‐06 ‐‐ 7.23E‐05 1.36E‐07 2.26E‐08 9.71E‐03 5.01E‐01 ‐‐ ‐‐ ‐‐ 4.56E‐07 ‐‐ ‐‐ ‐‐ ‐‐ 9.88E‐06 1.26E‐07 2.13E‐07 4.24E‐06 7.68E‐06 5.90E‐07 4.05E‐07 6.18E‐05 2.36E‐03 ‐‐ 4.14E‐03 9.91E‐06 1.26E‐06 7.27E‐06 5.75E‐08 7.32E‐07 2.26E‐04 0.5 Suburban Residential Garden Exposure Scenario Noncarcinogenic Carcinogenic Percent Contribution 1.1% 0.0% ‐‐ 0.0% 0.0% 0.0% 1.9% 95.8% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.5% ‐‐ 0.8% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 100.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ RBSLa (mg/kg) 7.51E‐09 ‐‐ 4.04E‐03 2.87E‐03 ‐‐ ‐‐ ‐‐ 9.92E‐05 8.05E‐04 8.09E‐05 8.05E‐04 ‐‐ 8.09E‐04 5.48E‐04 8.06E‐03 2.38E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.71E‐04 1.94E‐03 8.13E‐04 ‐‐ 5.42E‐05 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Cancer Risk 3.70E‐05 ‐‐ 2.31E‐08 8.64E‐07 ‐‐ ‐‐ ‐‐ 1.09E‐01 9.45E‐07 1.05E‐05 1.78E‐06 ‐‐ 1.73E‐06 1.31E‐07 1.45E‐07 3.01E‐06 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.21E‐07 2.84E‐04 8.43E‐07 ‐‐ 2.51E‐06 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1E‐01 Percent Contribution 0.0% ‐‐ 0.0% 0.0% ‐‐ ‐‐ ‐‐ 99.7% 0.0% 0.0% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.3% 0.0% ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100.0% RBSLa (mg/kg) 2.52E‐07 2.29E+00 ‐‐ 1.80E‐01 1.88E+01 1.01E+02 1.39E‐01 1.04E‐01 ‐‐ ‐‐ ‐‐ 1.08E+01 ‐‐ ‐‐ ‐‐ ‐‐ 3.61E+00 1.84E+00 1.77E+00 1.05E‐01 1.03E‐01 1.40E+01 1.30E+01 4.53E‐03 1.08E+00 ‐‐ 1.31E‐01 7.21E‐02 5.31E+00 1.58E‐02 1.01E+02 1.04E+01 1.81E+00 Hazard Index Hazard Quotient 1.10E+00 8.40E‐04 ‐‐ 1.38E‐02 2.15E‐05 3.70E‐06 1.84E+00 1.04E+02 ‐‐ ‐‐ ‐‐ 6.98E‐05 ‐‐ ‐‐ ‐‐ ‐‐ 1.67E‐03 2.81E‐05 4.95E‐05 8.27E‐04 1.53E‐03 9.26E‐05 6.78E‐05 1.22E‐02 5.13E‐01 ‐‐ 1.09E+00 1.88E‐03 1.62E‐04 2.45E‐02 9.37E‐06 1.16E‐04 2.88E‐02 108 Recreational Exposure Scenario Noncarcinogenic Carcinogenic Percent Contribution 1.0% 0.0% ‐‐ 0.0% 0.0% 0.0% 1.7% 95.7% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.5% ‐‐ 1.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 100.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ RBSLa (mg/kg) 1.80E‐05 ‐‐ 8.26E+00 5.83E+00 ‐‐ ‐‐ ‐‐ 2.46E‐01 9.39E‐01 9.39E‐02 9.39E‐01 ‐‐ 9.39E‐01 1.32E+00 9.39E+00 2.75E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.60E‐01 6.27E+00 9.39E‐01 ‐‐ 1.10E‐01 2.04E+02 ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Cancer Risk 1.54E‐08 ‐‐ 1.13E‐11 4.25E‐10 ‐‐ ‐‐ ‐‐ 4.41E‐05 8.10E‐10 9.02E‐09 1.52E‐09 ‐‐ 1.49E‐09 5.45E‐11 1.25E‐10 2.60E‐09 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.53E‐10 8.82E‐08 7.29E‐10 ‐‐ 1.23E‐09 4.22E‐12 ‐‐ ‐‐ ‐‐ ‐‐ 4E‐05 Percent Contribution 0.0% ‐‐ 0.0% 0.0% ‐‐ ‐‐ ‐‐ 99.7% 0.0% 0.0% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.2% 0.0% ‐‐ 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 100.0% RBSLa (mg/kg) 2.36E‐04 2.56E+03 ‐‐ 1.60E+02 1.49E+04 7.70E+04 1.23E+02 1.01E+02 ‐‐ ‐‐ ‐‐ 7.71E+03 ‐‐ ‐‐ ‐‐ ‐‐ 2.85E+03 1.92E+03 1.92E+03 9.61E+01 9.61E+01 1.03E+04 1.02E+04 4.16E+00 1.09E+03 ‐‐ 1.60E+02 6.40E+01 4.26E+03 2.49E+02 7.70E+04 7.71E+03 1.07E+03 Hazard Index Hazard Quotient 1.18E‐03 7.50E‐07 ‐‐ 1.55E‐05 2.72E‐08 4.83E‐09 2.08E‐03 1.07E‐01 ‐‐ ‐‐ ‐‐ 9.78E‐08 ‐‐ ‐‐ ‐‐ ‐‐ 2.12E‐06 2.69E‐08 4.57E‐08 9.08E‐07 1.65E‐06 1.26E‐07 8.62E‐08 1.32E‐05 5.05E‐04 ‐‐ 8.87E‐04 2.12E‐06 2.02E‐07 1.56E‐06 1.23E‐08 1.57E‐07 4.84E‐05 0.1 Percent Contribution 1.1% 0.0% ‐‐ 0.0% 0.0% 0.0% 1.9% 95.8% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.5% ‐‐ 0.8% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 100.0% Notes: a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory, Ventura County California (MWH, 2014). mg/kg = milligrams per kilogram TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0317151003RDD PAGE 1 OF 1 TABLE E1‐7 Chemical‐Specific Incremental Risk and Hazard Estimates for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Suburban Residential Soil Contact Exposure Scenario Analyte  2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   4,4'‐DDD   4,4'‐DDT   Acenaphthene   Acenaphthylene   Anthracene   Antimony   Aroclor 1254   Aroclor 1260   Arsenic   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   beta‐BHC   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Fluoranthene   Fluorene   Heptachlor epoxide   Hexavalent chromium   Indeno(1,2,3‐cd)pyrene   MCPA   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Styrene   Xylenes, Total  Notes: Total Site Cancer Hazard Risk Quotient 4.37E‐06 4.16E‐01 ‐‐ 5.83E‐05 7.31E‐10 ‐‐ 3.66E‐09 1.86E‐04 ‐‐ 3.44E‐06 ‐‐ 6.62E‐07 ‐‐ 3.09E‐06 ‐‐ 3.00E‐02 2.04E‐07 4.29E‐02 1.63E‐07 3.44E‐02 4.01E‐04 1.22E+00 1.12E‐06 ‐‐ 4.62E‐06 ‐‐ 9.30E‐07 ‐‐ ‐‐ 3.44E‐05 5.66E‐07 ‐‐ 1.85E‐09 ‐‐ 1.39E‐07 ‐‐ 9.27E‐08 ‐‐ ‐‐ 2.88E‐05 ‐‐ 1.34E‐06 ‐‐ 1.34E‐06 ‐‐ 2.43E‐05 ‐‐ 5.34E‐05 ‐‐ 3.77E‐04 ‐‐ 3.12E‐06 4.37E‐09 5.27E‐04 8.73E‐07 4.82E‐03 1.74E‐07 ‐‐ ‐‐ 2.74E‐02 9.08E‐10 9.31E‐06 5.60E‐08 1.34E‐04 1.10E‐10 2.36E‐06 ‐‐ 2.82E‐04 ‐‐ 1.33E‐05 ‐‐ 5.48E‐04 ‐‐ 2.47E‐03 ‐‐ 4.82E‐08 ‐‐ 8.69E‐07 Background Cancer Hazard Risk Quotient 5.77E‐08 5.50E‐03 ‐‐ 3.50E‐06 3.80E‐11 ‐‐ 1.43E‐09 7.23E‐05 ‐‐ ‐‐ ‐‐ 1.36E‐07 ‐‐ 2.26E‐08 ‐‐ 9.71E‐03 ‐‐ ‐‐ ‐‐ ‐‐ 1.65E‐04 5.01E‐01 1.97E‐09 ‐‐ 2.19E‐08 ‐‐ 3.69E‐09 ‐‐ ‐‐ 4.56E‐07 3.62E‐09 ‐‐ 1.83E‐10 ‐‐ 3.02E‐10 ‐‐ 6.32E‐09 ‐‐ ‐‐ 9.88E‐06 ‐‐ 1.26E‐07 ‐‐ 2.13E‐07 ‐‐ 4.24E‐06 ‐‐ 7.68E‐06 ‐‐ 5.90E‐07 ‐‐ 4.05E‐07 5.13E‐10 6.18E‐05 4.27E‐07 2.36E‐03 1.77E‐09 ‐‐ ‐‐ 4.14E‐03 ‐‐ ‐‐ 4.14E‐09 9.91E‐06 5.91E‐11 1.26E‐06 ‐‐ 7.27E‐06 ‐‐ 5.75E‐08 ‐‐ 7.32E‐07 ‐‐ 2.26E‐04 ‐‐ ‐‐ ‐‐ ‐‐ Incremental Cancer Percent Hazard Percent Risk Contribution Quotient Contribution 4.31E‐06 2% 4.10E‐01 33% ‐‐ ‐‐ 5.48E‐05 0% 6.93E‐10 0% ‐‐ ‐‐ 2.24E‐09 0% 1.13E‐04 0% ‐‐ ‐‐ 3.44E‐06 0% ‐‐ ‐‐ 5.26E‐07 0% ‐‐ ‐‐ 3.06E‐06 0% ‐‐ ‐‐ 2.03E‐02 2% 2.04E‐07 0% 4.29E‐02 3% 1.63E‐07 0% 3.44E‐02 3% 2.36E‐04 95% 7.20E‐01 57% 1.12E‐06 0% ‐‐ ‐‐ 4.60E‐06 2% ‐‐ ‐‐ 9.26E‐07 0% ‐‐ ‐‐ ‐‐ ‐‐ 3.39E‐05 0% 5.62E‐07 0% ‐‐ ‐‐ 1.67E‐09 0% ‐‐ ‐‐ 1.39E‐07 0% ‐‐ ‐‐ 8.64E‐08 0% ‐‐ ‐‐ ‐‐ ‐‐ 1.89E‐05 0% ‐‐ ‐‐ 1.21E‐06 0% ‐‐ ‐‐ 1.12E‐06 0% ‐‐ ‐‐ 2.01E‐05 0% ‐‐ ‐‐ 4.58E‐05 0% ‐‐ ‐‐ 3.77E‐04 0% ‐‐ ‐‐ 2.72E‐06 0% 3.86E‐09 0% 4.65E‐04 0% 4.46E‐07 0% 2.46E‐03 0% 1.73E‐07 0% ‐‐ ‐‐ ‐‐ ‐‐ 2.33E‐02 2% 9.08E‐10 0% 9.31E‐06 0% 5.19E‐08 0% 1.24E‐04 0% 5.13E‐11 0% 1.10E‐06 0% ‐‐ ‐‐ 2.74E‐04 0% ‐‐ ‐‐ 1.33E‐05 0% ‐‐ ‐‐ 5.47E‐04 0% ‐‐ ‐‐ 2.25E‐03 0% ‐‐ ‐‐ 4.82E‐08 0% ‐‐ ‐‐ 8.69E‐07 0% Recreational Exposure Scenario Total Site Cancer Hazard Risk Quotient 1.17E‐06 8.91E‐02 ‐‐ 1.25E‐05 2.18E‐10 ‐‐ 1.09E‐09 3.98E‐05 ‐‐ 7.26E‐07 ‐‐ 1.32E‐07 ‐‐ 6.59E‐07 ‐‐ 6.43E‐03 8.39E‐08 9.20E‐03 6.72E‐08 7.37E‐03 1.07E‐04 2.61E‐01 4.62E‐07 ‐‐ 1.91E‐06 ‐‐ 3.83E‐07 ‐‐ ‐‐ 7.37E‐06 2.33E‐07 ‐‐ 5.52E‐10 ‐‐ 5.73E‐08 ‐‐ 3.82E‐08 ‐‐ ‐‐ 6.17E‐06 ‐‐ 2.86E‐07 ‐‐ 2.86E‐07 ‐‐ 5.21E‐06 ‐‐ 1.15E‐05 ‐‐ 8.08E‐05 ‐‐ 6.64E‐07 1.30E‐09 1.13E‐04 1.80E‐07 1.03E‐03 7.19E‐08 ‐‐ ‐‐ 5.87E‐03 7.28E‐11 1.49E‐06 1.67E‐08 2.87E‐05 7.89E‐12 3.78E‐07 ‐‐ 6.04E‐05 ‐‐ 2.85E‐06 ‐‐ 1.17E‐04 ‐‐ 5.30E‐04 ‐‐ 8.44E‐09 ‐‐ 6.54E‐08 Background Cancer Hazard Risk Quotient 1.54E‐08 1.18E‐03 ‐‐ 7.50E‐07 1.13E‐11 ‐‐ 4.25E‐10 1.55E‐05 ‐‐ ‐‐ ‐‐ 2.72E‐08 ‐‐ 4.83E‐09 ‐‐ 2.08E‐03 ‐‐ ‐‐ ‐‐ ‐‐ 4.41E‐05 1.07E‐01 8.10E‐10 ‐‐ 9.02E‐09 ‐‐ 1.52E‐09 ‐‐ ‐‐ 9.78E‐08 1.49E‐09 ‐‐ 5.45E‐11 ‐‐ 1.25E‐10 ‐‐ 2.60E‐09 ‐‐ ‐‐ 2.12E‐06 ‐‐ 2.69E‐08 ‐‐ 4.57E‐08 ‐‐ 9.08E‐07 ‐‐ 1.65E‐06 ‐‐ 1.26E‐07 ‐‐ 8.62E‐08 1.53E‐10 1.32E‐05 8.82E‐08 5.05E‐04 7.29E‐10 ‐‐ ‐‐ 8.87E‐04 ‐‐ ‐‐ 1.23E‐09 2.12E‐06 4.22E‐12 2.02E‐07 ‐‐ 1.56E‐06 ‐‐ 1.23E‐08 ‐‐ 1.57E‐07 ‐‐ 4.84E‐05 ‐‐ ‐‐ ‐‐ ‐‐ Incremental Cancer Percent Hazard Percent Risk Contribution Quotient Contribution 1.15E‐06 2% 8.79E‐02 33% ‐‐ ‐‐ 1.17E‐05 0% 2.07E‐10 0% ‐‐ ‐‐ 6.67E‐10 0% 2.43E‐05 0% ‐‐ ‐‐ 7.26E‐07 0% ‐‐ ‐‐ 1.05E‐07 0% ‐‐ ‐‐ 6.54E‐07 0% ‐‐ ‐‐ 4.35E‐03 2% 8.39E‐08 0% 9.20E‐03 3% 6.72E‐08 0% 7.37E‐03 3% 6.33E‐05 93% 1.54E‐01 57% 4.61E‐07 1% ‐‐ ‐‐ 1.90E‐06 3% ‐‐ ‐‐ 3.82E‐07 1% ‐‐ ‐‐ ‐‐ ‐‐ 7.27E‐06 0% 2.32E‐07 0% ‐‐ ‐‐ 4.98E‐10 0% ‐‐ ‐‐ 5.71E‐08 0% ‐‐ ‐‐ 3.56E‐08 0% ‐‐ ‐‐ ‐‐ ‐‐ 4.05E‐06 0% ‐‐ ‐‐ 2.59E‐07 0% ‐‐ ‐‐ 2.41E‐07 0% ‐‐ ‐‐ 4.30E‐06 0% ‐‐ ‐‐ 9.81E‐06 0% ‐‐ ‐‐ 8.07E‐05 0% ‐‐ ‐‐ 5.78E‐07 0% 1.15E‐09 0% 9.97E‐05 0% 9.21E‐08 0% 5.27E‐04 0% 7.11E‐08 0% ‐‐ ‐‐ ‐‐ ‐‐ 4.98E‐03 2% 7.28E‐11 0% 1.49E‐06 0% 1.55E‐08 0% 2.66E‐05 0% 3.67E‐12 0% 1.76E‐07 0% ‐‐ ‐‐ 5.88E‐05 0% ‐‐ ‐‐ 2.83E‐06 0% ‐‐ ‐‐ 1.17E‐04 0% ‐‐ ‐‐ 4.82E‐04 0% ‐‐ ‐‐ 8.44E‐09 0% ‐‐ ‐‐ 6.54E‐08 0% a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory, Ventura County California  (MWH, 2014). bgs = below ground surface mg/kg = milligrams per kilogram PCB = polychlorinated biphenyl TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0317151003RDD PAGE 1 OF 1 TABLE E1‐8 Risk Estimates for Exposure to Soil Radionuclides (0 to 2 feet bgs)  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analyte  Plutonium‐244   Strontium‐90   Thorium‐229   Yttrium‐90  Exposure Point  Concentration (EPC) (pCi/g) 2.20E‐03 2.75E‐01 4.54E‐02 2.75E‐01 Suburban Residential Soil Contact Exposure Scenario Carcinogenic Cancer Percent RBSLa (pCi/g) Risk Contribution 6.36E‐02 3.46E‐08 19.6% 7.22E+00 3.81E‐08 21.6% 4.37E‐01 1.04E‐07 58.8% 2.20E+03 1.25E‐10 0.1% 2E‐07 100.0% Total Risk Suburban Residential Garden Exposure Scenario Carcinogenic Cancer Percent RBSLa (pCi/g) Risk Contribution 6.22E‐02 3.54E‐08 14.3% 3.85E+00 7.15E‐08 28.8% 3.22E‐01 1.41E‐07 56.8% 2.20E+03 1.25E‐10 0.1% Total Risk 2E‐07 100.0% Recreational Exposure Scenario Carcinogenic Cancer Percent RBSLa (pCi/g) Risk Contribution 3.09E‐01 7.12E‐09 19.6% 3.50E+01 7.86E‐09 21.6% 2.12E+00 2.14E‐08 58.8% 1.07E+04 2.57E‐11 0.1% Total Risk 4E‐08 100.0% Notes: a  RBSL =  risk‐based screening level derived per e‐mail communication from Mike Bower/Boeing to Roger Paulson/DTSC, dated January 14, 2015. bgs ‐ below ground surface EN0317151003RDD PAGE 1 OF 1 TABLE E1‐9 Risk and Hazard Estimates for Exposure to Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Exposure Point  Concentration (µg/L) Analyte  1,1,1‐Trichloroethane  9.63E‐01  1,1,2‐Trichloro‐1,2,2‐trifluoroethan 2.45E‐01  Benzene  1.30E‐01  Chloroform  2.10E‐03  Dichlorodifluoromethane  1.40E‐03  Ethylbenzene  1.09E‐01  Tetrachloroethene  9.50E‐03  Toluene  1.98E‐01  Trichloroethene  1.49E+01  Trichlorofluoromethane  2.20E‐02  Xylenes, Total  1.28E‐01 Exposure Point  Concentration (µg/m3) 9.63E+02 2.45E+02 1.30E+02 2.10E+00 1.40E+00 1.09E+02 9.50E+00 1.98E+02 1.49E+04 2.20E+01 1.28E+02 Carcinogenic RBSLa (µg/m3) ‐‐ ‐‐ 8.39E+01 4.59E+02 ‐‐ 9.73E+02 9.36E+03 ‐‐ 5.93E+02 ‐‐ ‐‐ Total Risk Suburban Residential Indoor Air Exposure Scenario Noncarcinogenic Cancer Risk ‐‐ ‐‐ 1.55E‐06 4.58E‐09 ‐‐ 1.12E‐07 1.01E‐09 ‐‐ 2.51E‐05 ‐‐ ‐‐ 3E‐05 Percent Contribution ‐‐ ‐‐ 5.8% 0.0% ‐‐ 0.4% 0.0% ‐‐ 93.8% ‐‐ ‐‐ 100.0% RBSLa (µg/m3) 1.04E+06 3.13E+07 6.26E+04 3.13E+05 1.04E+05 2.09E+06 4.17E+04 3.13E+05 2.09E+03 7.30E+05 7.30E+05 Hazard Index Hazard Quotient 9.26E‐04 7.83E‐06 2.08E‐03 6.71E‐06 1.35E‐05 5.22E‐05 2.28E‐04 6.33E‐04 7.13E+00 3.01E‐05 1.75E‐04 7 Percent Contribution 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 99.9% 0.0% 0.0% 100.0% Notes: a  RBSL =  risk‐based screening level from the Appendix A of the Comprehensive Data Quality Objectives Report, RCRA Facility Investigation, Santa Susana Field Laboratory,  Ventura County, California  (CH2M HILL, 2013a). µg/L ‐ micrograms per liter 3 µg/m  ‐ micrograms per cubic meter EN0317151003RDD PAGE 1 OF 1 TABLE E1‐10 Risk and Hazard Estimates for Exposure to Chatsworth Groundwater (Domestic use at Well HAR‐18) RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, Calif Analyte 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,4‐Dioxane 2,3,7,8‐TCDD TEQ Acetone Aldrin alpha‐BHC Beryllium bis(2‐Ethylhexyl) phthalate cis‐1,2‐Dichloroethene Copper Dibromomethane Ethylene Formaldehyde gamma‐BHC Heptachlor Manganese Naphthalene n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine Selenium Thallium Tin trans‐1,2‐Dichloroethene Trichloroethene Vinyl chloride Exposure Point  Concentration (µg/L) 7.10E+02 5.20E+00 2.40E+01 6.10E+00 1.40E+01 1.20E‐08 7.10E+01 1.20E‐02 3.70E‐03 5.80E‐02 4.00E+00 1.70E+03 2.88E+01 4.90E‐01 3.00E+00 3.20E+01 1.30E‐01 4.40E‐02 1.50E+02 1.10E‐02 3.60E+00 4.10E‐03 2.70E+00 4.80E‐02 1.20E+01 4.60E+01 6.50E+02 3.60E+02 Carcinogenic RBCb (µg/L) ‐‐ 2.51E+00 ‐‐ 2.19E‐01 2.47E+00 5.15E‐07 ‐‐ 3.94E‐03 1.42E‐02 ‐‐ 2.23E+01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.49E‐02 1.86E‐03 ‐‐ 1.53E‐01 1.51E‐03 9.25E‐03 ‐‐ ‐‐ ‐‐ ‐‐ 4.24E‐01 1.36E‐02 Total Risk Cancer Risk ‐‐ 2.07E‐06 ‐‐ 2.79E‐05 5.67E‐06 2.33E‐08 ‐‐ 3.05E‐06 2.61E‐07 ‐‐ 1.79E‐07 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3.72E‐06 2.37E‐05 ‐‐ 7.19E‐08 2.38E‐03 4.43E‐07 ‐‐ ‐‐ ‐‐ ‐‐ 1.53E‐03 2.65E‐02 3E‐02 Suburban Residential Exposure Scenarioa Noncarcinogenic b RBC Percent Contribution (µg/L) ‐‐ 5.50E+04 0.0% 1.05E+03 ‐‐ 1.26E+02 0.1% 3.88E+01 0.0% 6.00E+02 0.0% 2.01E‐05 ‐‐ 1.41E+04 0.0% 6.02E‐01 0.0% 9.72E+01 ‐‐ 2.46E+01 0.0% 4.01E+02 ‐‐ 1.04E+01 ‐‐ 7.99E+02 ‐‐ 8.00E+00 ‐‐ 6.26E+03 ‐‐ 3.96E+03 0.0% 3.64E+00 0.1% 1.28E+00 ‐‐ 4.33E+02 0.0% 1.75E+01 7.8% 1.60E‐01 0.0% ‐‐ ‐‐ 9.98E+01 ‐‐ 2.00E‐01 ‐‐ 1.20E+04 ‐‐ 9.29E+01 5.0% 2.82E+00 86.9% 4.44E+01 100.0% Hazard Index Hazard Quotient 1.29E‐02 4.95E‐03 1.90E‐01 1.57E‐01 2.33E‐02 5.97E‐04 5.04E‐03 1.99E‐02 3.81E‐05 2.36E‐03 9.98E‐03 1.63E+02 3.60E‐02 6.13E‐02 4.79E‐04 8.08E‐03 3.57E‐02 3.44E‐02 3.46E‐01 6.29E‐04 2.25E+01 ‐‐ 2.71E‐02 2.40E‐01 1.00E‐03 4.95E‐01 2.30E+02 8.11E+00 426 Percent Contribution 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 38.3% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.1% 0.0% 5.3% ‐‐ 0.0% 0.1% 0.0% 0.1% 54.1% 1.9% 100.0% Notes: a  Risk and hazard estimates are provided for the Chatsworth Formation groundwater well with the highest risk within a Subarea 5/9 South. b  RBC =  Risk‐based concentration computed using the USEPA’s Regional Screening Level online calculator (USEPA, 2014), with some exposure parameters changed from their  current USEPA default values (as described in Section 1.5 of Appendix C). µg/L ‐ micrograms per liter TEQ = 2,3,7,8‐TCDD toxicity equivalents USEPA = United States Environmental Protection Agency EN0317151003RDD PAGE 1 OF 1 TABLE E1‐11 Risk Estimates for Exposure to Radionuclides in Chatsworth Groundwater (Domestic use at Well HAR‐18) RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analyte Uranium‐233/234, Dissolved Uranium‐235, Dissolved Exposure Point  Concentration (pCi/L) 8.90E+00 5.60E‐01 Suburban Residential Exposure Scenario Carcinogenic RBSLa Cancer Percent (pCi/L) Risk Contribution 6.15E‐01 1.45E‐05 94.1% 6.15E‐01 9.11E‐07 5.9% Total Risk 2E‐05 100.0% Notes:  RBSL =  risk‐based screening level derived per e‐mail communication from Mike Bower/Boeing to Roger Paulson/DTSC, dated January  14, 2015. pCi/L = picocuries per liter a EN0317151003RDD PAGE 1 OF 1 TABLE E1‐12 Human Health Risk Assessment Uncertainty Analysis RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Assessment  Element COPC Selection Uncertainty Several chemicals were selected as a COPC since it could not be demonstrated to be consistent with background  concentrations through the Wilcoxon Rank Sum test. For site data sets that are small, uncertainty is introduced into  the comparisons.  Magnitude of Impact Moderate Direction of Impact Conservative Moderate Conservative Volatile organic chemicals detected in soil vapor were selected as COPCs. Soil vapor is anticipated to reflect the sum  total of vapor contributions originating from soil and/or groundwater beneath the site. Low Realistic Petroleum hydrocarbons were not selected as COPCs since TPH‐related constituents (BTEX and PAHs) were analyzed  for and evaluated for selection as COPCs. Exposure Pathways Since Boeing plans for the future use of their property as open space, the most likely future use of SSFL is for  recreational purposes, which has lower risks than for hypothetical suburban residential. COCs, however, have been  identified for both recreational and suburban residential scenarios. Low Realistic Moderate Conservative Risk estimates for fruit and vegetable consumption are based on conservative models that are based on associations  with physical‐chemical properties, such as Koc.  Risks associated with drinking of groundwater are not realistic because the groundwater beneath the SSFL is not  currently used as a drinking water source, and the presence of the contamination will likely require a restriction on its  future use as well. EPCs are based on some data that are over 10 years old. In these cases, available analytical data may not accurately  reflect current site conditions. Source concentrations assumed constant over time. Chemical concentrations may  decline as a result of migration or degradation. Moderate Conservative High Conservative Low Conservative Use of UCLs and maximum detected concentrations will likely overestimate site risks. The 95% UCL concentration of some chemicals is greater than the maximum concentration; therefore, the maximum  was used as the EPC. This is considered to be a likely overestimation of the representative EPC because samples were  collected in areas with the highest likelihood to detect the highest concentrations at the site. Low Moderate Conservative Conservative When groundwater monitoring data were reported as both total (unfiltered) and dissolved (filtered) concentrations,  the highest value was used for the HHRA. Although dissolved concentrations represent the concentrations that may  migrate, the total concentration in groundwater may be greater when there are significant amount of suspended  solids present. The maximum detected concentration of each COPC detected in groundwater at the maximum risk well point within  Subarea 5/9 South over the last 3 years of available data was used as the EPC. Moderate Realistic Moderate Conservative The extrapolation of soil Aroclor‐1254 and Aroclor‐1260 concentrations to individual PCB congener concentrations  introduces some uncertainty into the EPC estimates for the PCB congeners. Low Conservative Vapor migration into indoor air has been estimated using default soil vapor‐to‐indoor air attenuation factors.  Migration to indoor air assumes an infinite source and that vapor concentrations remain constant over the 30‐year  duration of exposure for a hypothetical suburban resident. Moderate Uncertain Some chemicals were selected as COPCs due to exceeding two times the background level, however were not  statistically different from background concentrations through the Wilcoxon Rank Sum test. Inclusion of these as  COPCs could overestimate risks or hazards. EPC Calculations EN0317151003RDD PAGE 1 OF 2 TABLE E1‐12 Human Health Risk Assessment Uncertainty Analysis RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Assessment  Element Toxicity Factors Uncertainty Toxicity factors used for this HHRA are from the SRAM Rev. 2 Addendum (for soil; MWH, 2014a) and Appendix A to  the Comprehensive Data Quality Objectives Report (for soil vapor; CH2M HILL, 2013c). Changes to toxicity factors  occurring subsequent to the date of these sources will be considered during the CMS, as needed. Magnitude of Impact Uncertain Direction of Impact Uncertain High Conservative Assumes that all carcinogens do not have a threshold below which carcinogenic response occurs and, therefore, any  dose, no matter how small, results in some potential risk. Moderate Conservative Not all slope factors represent the same degree of certainty, and all are subject to change as new evidence becomes  available. Some slope factors derived by OEHHA are considerably more conservative than corresponding factors  derived by USEPA (e.g., arsenic, PCBs). The arsenic RBSL used in this HHRA is about an order of magnitude lower than  the USEPA value. Since arsenic is identified as the primary COC for soil at the EEL RFI site, risks could be as much as  tenfold lower if the USEPA value were used. High Conservative Cancer slope factors derived from animal studies are the upper‐bound maximum likelihood estimates based on a  linear dose‐response curve, and therefore, overstate carcinogenic potency. Moderate Conservative No dermal toxicity values are available, oral toxicity factors are used for the dermal route.  Moderate Conservative High degree of uncertainty in extrapolation of dose‐response data from laboratory animals to humans. High Conservative Risk estimates for both chemicals and radionuclides are estimated for COPC/ROPCs. These risk estimates are  reported separately due to the different uncertainties associated with each. ROPCs identified for Subarea 5/9 South  Chatsworth Formation groundwater include uranium‐233/234 and uranium‐235. Since background levels of these  ROPCs in groundwater are not available, some portion of the levels detected may reflect natural levels. High Conservative Extrapolation of dose‐response data from laboratory animals to humans. Risk  Characterization Notes: BTEX = benzene, toluene, ethylbenzene, and xylenes COC = chemical of concern COPC = chemical of potential concern CMS = corrective measure study EEL = Environmental Effect Laboratory EPC = exposure point concentration HHRA = human health risk assessment PAH = polycyclic aromatic hydrocarbon PCB = polychlorinated biphenyls RBSL = risk‐based screening level  ROPC = radionuclide of potential concern TPH = total petroleum hydrocarbons UCL = upper confidence limit    USEPA = United States Environmental Protection Agency EN0317151003RDD PAGE 2 OF 2 Figure FIGURE E1‐1 Conceptual Exposure Model for Potential Human Receptors      RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California SECONDARY SOURCE SECONDARY RELEASE MECHANISM TERTIARY SOURCE VOLATILIZATION AND EROSION DUST AND VAPOR EMISSIONS ROOT UPTAKE FROM SOIL EDIBLE VEGETATION EXPOSURE ROUTE POSSIBLE RECEPTORS STORAGE SPILLS DUST INHALATION VAPOR INHALATIONa ACCIDENTAL SPILLS AND RELEASES INGESTIONb BELOW GROUND OR ABOVE GROUND STORAGE TANKS LEAKAGE DUMPS AND SUMPS SOIL AND/OR WEATHERED BEDROCK SOIL, EPHEMERAL SEDIMENT, AND WEATHERED BEDROCK EROSION, RESUSPENSION, AND  SURFACE FLOW DEBRIS AREAS, ROCKET TESTING, RANGES, AND DRAINAGES LEACHING, INFILTRATION, AND PERCOLATION SEDIMENT AND SURFACE WATER INGESTION DERMAL ABSORPTION INHALATIONa                                      seeps/springs       LEACHING, INFILTRATION, AND  PERCOLATION WASTE  DISPOSAL AREAS INCIDENTAL INGESTION DERMAL ABSORPTION CHATSWORTH GROUNDWATER INGESTION DERMAL ABSORPTION INHALATION PRIOR WASTE DISPOSAL PRACTICES NOTES: a. Exposure is limited to volatile compounds; residential receptors include both indoor and outdoor air exposure to volatiles; recreator receptors include only outdoor air exposure. Inhalation exposure does not include groundwater to ambient air pathways because these pathways have been shown to be insignificant at the SSFL. b. Exposure includes the ingestion of homegrown fruits and/or vegetables and is limited to compounds that bioaccumulate. c. Groundwater risk estimates for each RFI site are based on the maximum risk well point within the entire subarea. ‐ Potentially complete exposure pathway evaluated in this risk assessment ‐ Incomplete exposure pathway not evaluated in this risk assessment RECREATOR PRIMARY RELEASE MECHANISM SUBURBAN  RESIDENT PRIMARY SOURCE Attachment 1 Attachment 1 Tables 1  2  3  4  5  6  7  14 Samples Included in the Human Health Risk Assessment  Comparison of Maximum Chemical Concentrations in Site Soil with Background Levels  Comparison of Maximum Radionuclide Concentrations in Site Soil with Background Levels  Results of Background Statistical Comparisons for Soil  Aroclor to PCB Congener Extrapolation  Risk and Hazard Estimates for Exposure to Soil (0 to 10 feet bgs)  Evaluation of Potential for Hotspots in Soil (0 to 10 feet bgs)  EN0411151012BAO ATTACHMENT 1, TABLE 1 Samples Included in the Human Health Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID Surface Soil 0‐2 feet bgs A3_SED_DG‐11 A3_SED_DG‐12 A3_SED_DG‐13 A3_SED_DG‐14 D‐3‐03 ELBS01 ELBS02 ELBS02 ELBS02 ELBS03 ELBS04 ELBS05 ELBS06 ELBS07 ELBS10 ELBS1003 ELBS1003 ELBS1004 ELBS1004 ELBS1005 ELBS1006 ELBS1007 ELBS1011 ELBS1012 ELBS1013 ELBS1014 ELBS1014 ELBS1015 ELBS1016 ELBS1017 ELBS1018 ELBS1018 ELBS1019 ELBS1020 ELBS1021 ELBS1024 ELBS1026 ELBS1027 ELBS1028 ELBS1028 ELBS1028 ELBS1029 EN0317151003RDD Sample ID Sample Date Sample Type SL‐011‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 D‐3‐03 RF246 RD247 RF247 RS691 RD976 RS504 RS505 RS645 RS646 RS887 ELBS1003S010 ELBS1003X010 ELBS1004D010 ELBS1004S010 ELBS1005S010 ELBS1006S010 ELBS1007S010 ELBS1011S010 ELBS1012S010 ELBS1013S010 ELBS1014S010 ELBS1014D010 ELBS1015S010 ELBS1016S010 ELBS1017S010 ELBS1018S010 ELBS1018D010 ELBS1019S010 ELBS1020S010 ELBS1021S010 ELBS1024S010 ELBS1026S010 ELBS1027S010 ELBS1028X010 ELBS1028D010 ELBS1028S010 ELBS1029X010 10/5/2011 10/5/2011 10/5/2011 10/5/2011 2/17/1993 11/11/1997 11/11/1997 11/11/1997 1/29/1998 12/2/1997 12/5/1997 12/5/1997 1/23/1998 1/23/1998 9/22/1999 4/8/2008 4/8/2008 4/8/2008 4/8/2008 4/10/2008 4/10/2008 4/8/2008 3/26/2008 3/26/2008 4/11/2008 3/24/2008 3/24/2008 4/8/2008 3/24/2008 3/24/2008 3/26/2008 3/26/2008 3/27/2008 4/1/2008 3/26/2008 3/27/2008 3/27/2008 3/26/2008 3/27/2008 3/27/2008 3/27/2008 3/24/2008 N N N N N N N N N N N N N N N N Split Sample FD N N N N N N N N FD N N N N FD N N N N N N Split Sample FD N Split Sample Start Depth  End Depth  (ft) (ft) 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Soil Contact Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Suburban Residential Vapor Intrusion  Garden Exposure Scenario Exposure Scenario ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Recreational Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X PAGE 1 OF 6 ATTACHMENT 1, TABLE 1 Samples Included in the Human Health Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID ELBS1029 ELBS13 ELBS14 ELBS1400 ELBS1400 ELBS1401 ELBS1402 ELBS1402 ELBS1403 ELBS1403 ELBS1405 ELBS2000 ELBS2000 ELBS2000 ELBS2001 ELBS2001 ELBS2002 ELBS2002 ELBS2003 ELBS2003 ELBS2004 ELBS2004 ELBS2005 ELBS2005 ELBS2005 ELBS2006 ELBS2006 ELBS2007 ELBS2007 ELBS2007 ELBS2008 ELBS2008 ELBS2008 ELBS2009 ELBS2009 ELBS2010 ELBS2010 ELBS2012 ELBS2012 ELBS2015 ELBS2017 ELBS2020 ELBS2020 EN0317151003RDD Sample ID ELBS1029S010 MT825 MT826 ELBS1400D01 ELBS1400S01 ELBS1401S01 ELBS1402S01 ELBS1402X01 ELBS1403D01 ELBS1403S01 ELBS1405S01 ELBS2000S001 ELBS2000D001 ELBS2000S002 ELBS2001S001 ELBS2001S002 ELBS2002S001 ELBS2002S002 ELBS2003S001 ELBS2003S002 ELBS2004S001 ELBS2004S002 ELBS2005S001 ELBS2005S002 ELBS2005S002SP ELBS2006S001 ELBS2006S002 ELBS2007S001SP ELBS2007S001 ELBS2007S002 ELBS2008S001 ELBS2008S002 ELBS2008D002 ELBS2009S001 ELBS2009S002 ELBS2010S001 ELBS2010S002 ELBS2012S001 ELBS2012S002 ELBS2015S001 ELBS2017S001 ELBS2020S001 ELBS2020S002 Sample Date 3/24/2008 9/17/2003 9/17/2003 5/23/2008 5/23/2008 5/23/2008 5/30/2008 5/30/2008 5/23/2008 5/23/2008 6/2/2008 6/18/2013 6/18/2013 6/18/2013 6/18/2013 6/18/2013 6/12/2013 6/12/2013 6/17/2013 6/17/2013 6/17/2013 6/17/2013 6/17/2013 6/17/2013 6/17/2013 6/13/2013 6/13/2013 6/19/2013 6/19/2013 6/19/2013 6/18/2013 6/18/2013 6/18/2013 6/12/2013 6/12/2013 6/20/2013 6/20/2013 6/20/2013 6/20/2013 6/17/2013 6/19/2013 6/17/2013 6/17/2013 Sample Type N N N FD N N N Split Sample FD N N N FD N N N N N N N N N N N Split Sample N N Split Sample N N N N FD N N N N N N N N N N Start Depth  End Depth  (ft) (ft) 0 1 0 0.5 0 0.5 0 1 0 1 0 1 0.5 1 0.5 1 0 1 0 1 0.5 1 0 0.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0.5 1.5 0 0.5 0 0.5 0.5 1.5 Soil Contact Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Suburban Residential Vapor Intrusion  Garden Exposure Scenario Exposure Scenario ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X Recreational Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X PAGE 2 OF 6 ATTACHMENT 1, TABLE 1 Samples Included in the Human Health Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID ELBS2021 ELBS2021 ELBS2022 ELBS2022 ELBS2022 ELBS2023 ELBS2024 ELBS2024 ELBS2025 ELBS2025 ELBS2026 ELBS2026 ELBS2028 ELBS2035 ELBS2036 ELBS3000 ELBS3001 ELBS3002 ELBS3003 ELBS3003 ELBS3003 ELBS3004 ELBS3005 ELBS3007 ELBS3007 ELBS3009 ELBS3010 ELBS3010 ELBS3011 ELBS3012 ELBS3015 ELBS3016 ELBS3016 ELBS3017 ELBS3020 ELBS3020 ELBS3021 ELBS3021 ELBS3022 ELBS3023 ELBS3023 ELBS3024 ELSS01 EN0317151003RDD Sample ID ELBS2021S001 ELBS2021S002 ELBS2022S001 ELBS2022D001 ELBS2022S002 ELBS2023S001 ELBS2024S001 ELBS2024S002 ELBS2025S001 ELBS2025S002 ELBS2026S001 ELBS2026S002 ELBS2028S001 ELBS2035S001 ELBS2036S001 ELBS3000S001 ELBS3001S001 ELBS3002S001 ELBS3003S001SP ELBS3003S001 ELBS3003S002 ELBS3004S001 ELBS3005S001 ELBS3007S001 ELBS3007S002 ELBS3009S001 ELBS3010S001 ELBS3010S002 ELBS3011S001 ELBS3012S001 ELBS3015S001 ELBS3016S001SP ELBS3016S001 ELBS3017S001 ELBS3020S001 ELBS3020S002 ELBS3021D001 ELBS3021S001 ELBS3022S001 ELBS3023S001SP ELBS3023S001 ELBS3024S001 EL1S1 Sample Date 6/18/2013 6/18/2013 6/18/2013 6/18/2013 6/18/2013 6/20/2013 6/14/2013 6/14/2013 6/14/2013 6/14/2013 6/11/2013 6/11/2013 6/11/2013 6/19/2013 6/20/2013 5/14/2014 5/13/2014 5/20/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/20/2014 5/20/2014 5/13/2014 5/13/2014 5/13/2014 5/14/2014 5/14/2014 5/13/2014 5/13/2014 5/13/2014 6/17/2014 6/17/2014 6/17/2014 6/17/2014 6/17/2014 6/17/2014 5/23/1996 Sample Type N N N FD N N N N N N N N N N N N N N Split Sample N N N N N N N N N N N N Split Sample N N N N FD N N Split Sample N N N Start Depth  End Depth  (ft) (ft) 0 0.5 0.5 1.5 0 0.5 0 0.5 0.5 1.5 0 0.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0.5 1.5 0 0.5 0 0.5 0 0.5 0 0.5 0.5 1.5 0.5 1.5 0 0.5 0 0.5 0.5 1.5 0.5 1.5 0.5 1.5 0 0.5 0.5 1 0 0.5 0 0.5 0.5 1.5 0.5 1.5 0 0.5 0 0.5 0 0.5 0 0.5 0 0.5 0 0.5 0.5 1.5 1 1.5 1 1.5 1 1.5 0 0.5 0 0.5 0 0.5 0 0.5 Soil Contact Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Suburban Residential Vapor Intrusion  Garden Exposure Scenario Exposure Scenario ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X Recreational Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X PAGE 3 OF 6 ATTACHMENT 1, TABLE 1 Samples Included in the Human Health Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID Sample ID GMBS2011E GMBS2011ES001 GMBS2012A GMBS2012AS001 GMBS2012A GMBS2012AS001SP GMBS2012B GMBS2012BS001 GMBS2012B GMBS2012BS001SP MH02072993 072993MH02 10244 SL‐143‐SA5C STBS1019 STBS1019S001 STBS3008 STBS3008S001 Subsurface Soil 2‐10 feet bgs ELBS02 RD248 ELBS02 RF248 ELBS05 RS647 ELBS1011 ELBS1011S060 ELBS1013 ELBS1013S060 ELBS1014 ELBS1014S050 ELBS1015 ELBS1015X060 ELBS1015 ELBS1015S060 ELBS1016 ELBS1016S060 ELBS1017 ELBS1017S060 ELBS1018 ELBS1018X060 ELBS1018 ELBS1018S060 ELBS1019 ELBS1019S060 ELBS1024 ELBS1024S060 ELBS1026 ELBS1026S060 ELBS1027 ELBS1027S060 ELBS1028 ELBS1028S060 ELBS1403 ELBS1403S02 ELBS1409 ELBS1409S01 ELBS1410 ELBS1410S01 ELBS2000 ELBS2000S003SP ELBS2000 ELBS2000S003 ELBS2000 ELBS2000S004 ELBS2001 ELBS2001S003 ELBS2002 ELBS2002S003 ELBS2003 ELBS2003S003 ELBS2004 ELBS2004S003 ELBS2005 ELBS2005D003 ELBS2005 ELBS2005S003 ELBS2006 ELBS2006S003 ELBS2006 ELBS2006S004 ELBS2007 ELBS2007S003 ELBS2008 ELBS2008S003 EN0317151003RDD Sample Date 1/27/2014 1/27/2014 1/27/2014 1/27/2014 1/27/2014 7/29/1993 20‐Oct‐10 5/22/2012 5/15/2014 Sample Type N N Split Sample N Split Sample N N N N 11/11/1997 11/11/1997 1/23/1998 3/26/2008 4/11/2008 3/24/2008 4/8/2008 4/8/2008 3/24/2008 3/24/2008 3/26/2008 3/26/2008 3/27/2008 3/27/2008 3/27/2008 3/26/2008 3/27/2008 5/23/2008 5/23/2008 5/27/2008 6/18/2013 6/18/2013 6/18/2013 6/18/2013 6/12/2013 6/17/2013 6/17/2013 6/17/2013 6/17/2013 6/13/2013 6/13/2013 6/19/2013 6/18/2013 N N N N N N Split Sample N N N Split Sample N N N N N N N N N Split Sample N N N N N N FD N N N N N Start Depth  End Depth  (ft) (ft) 0.5 1 0.7 1.2 0.7 1.2 0.6 1.1 0.6 1.1 0 0 0 0.5 1 1.5 0 0.5 6 6 4 5 5 4 5 5 5 4.75 5 5 5 5 5 5 5 3 4 5 5 5 9 5 5 3.5 5 5 5 5 9 4 9 6 6 4 6 6 5 6 6 6 5.75 6 6 6 6 6 6 6 4 5 6 6 6 10 6 6 4 6 6 6 6 10 5 10 Soil Contact Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X Suburban Residential Vapor Intrusion  Garden Exposure Scenario Exposure Scenario ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Recreational Exposure Scenario X X X X X X X X X ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ PAGE 4 OF 6 ATTACHMENT 1, TABLE 1 Samples Included in the Human Health Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID ELBS2009 ELBS2009 ELBS2012 ELBS2012 ELBS2012 ELBS2015 ELBS2016 ELBS2018 ELBS2020 ELBS2021 ELBS2022 ELBS2023 ELBS2024 ELBS2025 ELBS2026 ELBS2028 ELBS2028 ELBS2035 ELBS2036 ELBS3002 ELBS3002 ELBS3003 ELBS3003 ELBS3006 ELBS3007 ELBS3007 ELBS3008 ELBS3009 ELBS3011 ELBS3012 ELBS3015 ELBS3021 ELBS3024 STBS3008 STBS3008 SWBS1006 Soil Vapor ELSV01 ELSV02 ELSV03 ELSV08 ELSV1003 ELSV1004 EN0317151003RDD Sample ID ELBS2009S003 ELBS2009D003 ELBS2012S003SP ELBS2012S003 ELBS2012S004 ELBS2015S002 ELBS2016S001 ELBS2018S001 ELBS2020S003 ELBS2021S003 ELBS2022S003 ELBS2023S002 ELBS2024S003 ELBS2025S003 ELBS2026S003 ELBS2028S002 ELBS2028S003 ELBS2035S002 ELBS2036S002 ELBS3002S002 ELBS3002S003 ELBS3003S003 ELBS3003S004 ELBS3006S001 ELBS3007S003 ELBS3007D003 ELBS3008S001 ELBS3009S002 ELBS3011S002 ELBS3012S002 ELBS3015S002 ELBS3021S002 ELBS3024S002 STBS3008S002 STBS3008S002SP SWBS1006S001 Sample Date 6/12/2013 6/12/2013 6/20/2013 6/20/2013 6/20/2013 6/17/2013 6/14/2013 6/13/2013 6/17/2013 6/18/2013 6/18/2013 6/20/2013 6/14/2013 6/14/2013 6/11/2013 6/11/2013 6/11/2013 6/19/2013 6/20/2013 5/20/2014 5/20/2014 5/13/2014 5/13/2014 5/14/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 5/13/2014 6/17/2014 6/17/2014 5/15/2014 5/15/2014 9/16/2008 Sample Type N FD Split Sample N N N N N N N N N N N N N N N N N N N N N N FD N N N N N N N N Split Sample N RV434 RV486 RV488 RV733 ELSV1003S050 ELSV1004S050 7/11/1997 7/17/1997 7/17/1997 9/29/1999 3/26/2008 3/26/2008 N N N N N N Start Depth  End Depth  (ft) (ft) 5 6 5 6 5 6 5 6 9 10 4 5 5 6 5 6 5 6 5 6 5 6 3.5 4 5 6 5 6 5 6 5 6 8.5 9 5.5 6.5 5.5 6.5 5 6 9 10 5 6 9 10 5 6 5 6 5 6 9.2 9.8 5 6 5 6 5 6 5 5.5 3 3.5 3 3.5 5 6 5 6 5.5 6.5 5 6 8 5 4 4 5 6 8 5 5 5 Soil Contact Exposure Scenario X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X X ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Suburban Residential Vapor Intrusion  Garden Exposure Scenario Exposure Scenario ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ X X X X X X ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Recreational Exposure Scenario ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ PAGE 5 OF 6 ATTACHMENT 1, TABLE 1 Samples Included in the Human Health Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID Sample ID ELSV1004 ELSV1004D050 ELSV1400 ELSV1400S01 ELSV1401 ELSV1401S01 ELSV1401 ELSV1401D01 ELSV1402 ELSV1402S01 ELSV1403 ELSV1403S01 ELSV2000 ELSV2000S001 ELSV2001 ELSV2001S001 ELSV2002 ELSV2002S001 ELSV2003 ELSV2003S001 ELSV2004 ELSV2004S001 ELSV2006 ELSV2006S001SP ELSV2006 ELSV2006S001 ELSV2008 ELSV2008S001 ELSV2009 ELSV2009S001 ELSV2011 ELSV2011S001 ELSV2012 ELSV2012S001 ELSV2013 ELSV2013S001 ELSV2013 ELSV2013D001 ELSV2014 ELSV2014S001 ELSV2016 ELSV2016S001 ELSV2018 ELSV2018S001 ELSV3000 ELSV3000S001 SWSV1006 SWSV1006S001 Notes: "‐‐" = not available bgs = below ground surface FD = field duplicate ft = feet N = normal sample X = Sample results used for this exposure scenario EN0317151003RDD Sample Date 3/26/2008 4/28/2008 4/28/2008 4/28/2008 5/16/2008 5/16/2008 8/5/2013 8/5/2013 8/7/2013 8/5/2013 8/5/2013 8/5/2013 8/5/2013 8/7/2013 8/5/2013 8/5/2013 8/5/2013 8/5/2013 8/5/2013 8/5/2013 8/5/2013 8/5/2013 5/23/2014 9/25/2008 Sample Type FD N N FD N N N N N N N Split Sample N N N N N N FD N N N N N Start Depth  End Depth  (ft) (ft) 4 5 4 5 4 5 4 5 4 5 4 5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 9.5 10 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 5 5.5 4 5 Soil Contact Exposure Scenario ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Suburban Residential Vapor Intrusion  Garden Exposure Scenario Exposure Scenario X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ X ‐‐ Recreational Exposure Scenario ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ PAGE 6 OF 6 ATTACHMENT 1, TABLE 2 Comparison of Maximum Chemical Concentrations in Site Soil with Background Levels RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical 1‐Methyl naphthalene 2,3,7,8‐TCDD TEQ 2,4,5‐TP (Silvex) 2,4‐Dichlorophenoxybutyric acid 2‐Methylnaphthalene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Acenaphthene Acenaphthylene Aluminum Anthracene Antimony Arsenic Barium Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Beryllium beta‐BHC bis(2‐Ethylhexyl) phthalate Boron Butyl benzyl phthalate Cadmium Chromium Chrysene Cobalt Copper Dibenzo(a,h)anthracene Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Fluoranthene Fluorene Fluoride Heptachlor Heptachlor epoxide Hexavalent Chromium Indeno(1,2,3‐cd)pyrene Iron Lead Lithium EN0317151003RDD Background Concentrationa (mg/kg) 0.0018 0.000000563 0.000322 0.027 0.0018 0.000186 0.004164 0.006101 0.0018 0.000815 37,900 0.000645 0.497 24.2 203.8 0.001222 0.00164 0.003264 0.001177 0.00353 1.424 0.000126 0.028 18.85 0.043 0.435 60.11 0.002457 26.18 42 0.00102 0.0995 0.00837 0.00637 0.0000826 0.000178 0.000159 0.00037 0.002466 0.001805 5.387 0.000116 0.00011 1.129 0.000792 46,671 33.9 64.4 Maximum  Concentration (mg/kg) 0.0012 0.0000519 ND 0.032 0.0015 0.0018 0.0029 0.019 0.017 0.0021 33,200 0.13 7.5 110 189 1.2 0.74 1 0.23 0.52 1.3 0.00073 0.0287 9.99 0.013 0.751 32.9 1.5 12.7 25.6 0.096 0.00597 0.0023 0.099 0.00055 0.00055 0.0005 0.0011 2.3 0.015 3.1 ND 0.00047 3.2 0.26 #N/A 16.5 33.6 0 to 2 ft bgs Maximum Exceeds Background? No Yes ND Yes No Yes No Yes Yes Yes No Yes Yes Yes No Yes Yes Yes Yes Yes No Yes Yes No No Yes No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes No ND Yes Yes Yes #N/A No No Maximum Exceeds 2X Background? No Yes ND No No Yes No Yes Yes Yes No Yes Yes Yes No Yes Yes Yes Yes Yes No Yes No No No No No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes No ND Yes Yes Yes #N/A No No Considered COPC? No Yes No See Background Statistics No Yes No Yes Yes Yes No Yes Yes Yes No Yes Yes Yes Yes Yes No Yes See Background Statistics No No See Background Statistics No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes #N/A No No Maximum  Concentration (mg/kg) 0.0012 0.0000519 0.0014 0.032 0.012 0.0018 0.0029 0.019 0.017 0.0021 33,200 0.13 7.5 110 230 1.2 0.74 1 0.23 0.52 1.9 0.00073 0.0503 10.1 0.013 0.751 38.5 1.5 18.5 25.6 0.096 0.00597 0.0023 0.099 0.00055 0.00055 0.0005 0.0011 2.3 0.015 11.2 0.00058 0.00047 3.2 0.26 #N/A 16.5 58 0 to 10 ft bgs Maximum Exceeds Background? No Yes Yes Yes Yes Yes No Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes #N/A No No Maximum Exceeds 2X Background? No Yes Yes No Yes Yes No Yes Yes Yes No Yes Yes Yes No Yes Yes Yes Yes Yes No Yes No No No No No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes #N/A No No Considered COPC? No Yes Yes See Background Statistics Yes Yes No Yes Yes Yes No Yes Yes Yes See Background Statistics Yes Yes Yes Yes Yes See Background Statistics Yes See Background Statistics No No See Background Statistics No Yes No No Yes No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes #N/A No No PAGE 1 OF 2 ATTACHMENT 1, TABLE 2 Comparison of Maximum Chemical Concentrations in Site Soil with Background Levels RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Chemical Background Concentrationa (mg/kg) 723 0.398 0.028 0.000279 1.642 0.0017 64.2 0.000649 0.001864 0.002586 0.536 0.095 79.1 0.629 3.83 111.8 153 10.64 Maximum  Concentration (mg/kg) 887 0.94 0.033 0.0047 0.961 0.0022 24.7 0.024 0.91 2.5 0.39 3.5 31.5 0.419 ND 58.9 126 5.74 0 to 2 ft bgs Maximum Exceeds Background? Yes Yes Yes Yes No Yes No Yes Yes Yes No Yes No No ND No No No Manganese MCPA Mercury Mirex Molybdenum Naphthalene Nickel Perchlorate Phenanthrene Pyrene Selenium Silver Strontium Thallium Tin Vanadium Zinc Zirconium Notes: a  Source: Based on data from the Final Chemical Soil Background Study Report  (DTSC, 2012). "‐‐" = not applicable bgs = below ground surface COPC = chemical of potential concern ft = feet mg/kg = milligrams per kilogram ND = not detected TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0317151003RDD Maximum Exceeds 2X Background? No Yes No Yes No No No Yes Yes Yes No Yes No No ND No No No Considered COPC? See Background Statistics Yes See Background Statistics Yes No See Background Statistics No Yes Yes Yes No Yes No No No No No No Maximum  Concentration (mg/kg) 887 0.94 0.033 0.0047 0.961 0.0022 32.2 0.043 0.91 2.5 0.76 3.5 41.3 0.427 0.384 73 126 8.19 0 to 10 ft bgs Maximum Exceeds Background? Yes Yes Yes Yes No Yes No Yes Yes Yes Yes Yes No No No No No No Maximum Exceeds 2X Background? No Yes No Yes No No No Yes Yes Yes No Yes No No No No No No Considered COPC? See Background Statistics Yes See Background Statistics Yes No See Background Statistics No Yes Yes Yes See Background Statistics Yes No No No No No No PAGE 2 OF 2 ATTACHMENT 1, TABLE 3 Comparison of Maximum Radionuclide Concentrations in Site Soil with Background Levels RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Concentration (mg/kg) 2.1 0.0142 0.0134 0.254 0.146 1.67 1.53 0.023 0.157 0.0147 0.156 2.48 1.64 0.00936 0.0014 26 2.01 1.6 0.0512 0.0595 0.803 2.995 0.0333 1.64 2.359 2.339 1.545 0.101 1.52 a 0 to 2 ft bgs Maximum Maximum Maximum  Exceeds 2X Exceeds Concentration Background? Background? (mg/kg) 1.32 No No 0.0135 No No 0.0129 No No 0.119 No No 0.0267 No No 1.1 No No 0.99 No No 0.0109 No No 0.0446 No No 0.0128 No No 0.089 No No 1.64 No No 1.06 No No 0.00783 No No 0.0022 Yes No 20.1 No No 1.37 No No 1 No No 0.275 Yes Yes 0.0276 No No 0.545 No No 1.25 No No 0.0454 Yes No 0.958 No No 1.23 No No 1.76 No No 0.852 No No 0.0564 No No 0.837 No No Radionuclide Actinium‐228 Americium‐241 Americium‐243 Antimony‐125 Barium‐137 Bismuth‐212 Bismuth‐214 Cesium‐134 Cesium‐137 Curium‐243/244 Europium‐155 Lead‐212 Lead‐214 Plutonium‐239/240 Plutonium‐244 Potassium‐40 Radon‐220 Radon‐222 Strontium‐90 Tellurium‐125 Thallium‐208 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Uranium‐233/234 Uranium‐235/236 Uranium‐238 Notes: a  Source: Based on data from the Final Chemical Soil Background Study Report (DTSC, 2012). bgs = below ground surface ft = feet pCi/g = picocuries per gram ROPC = radionuclide of potential concern EN0317151003RDD Considered ROPC? No No No No No No No No No No No No No No Yes No No No Yes No No No Yes No No No No No No 0 to 10 ft bgs Maximum Maximum Maximum  Exceeds 2X Exceeds Concentration Background? Background? (mg/kg) 1.32 No No 0.0135 No No 0.0129 No No 0.119 No No 0.0267 No No 1.1 No No 0.99 No No 0.0109 No No 0.0446 No No 0.0128 No No 0.089 No No 1.64 No No 1.06 No No 0.00783 No No 0.0022 Yes No 20.1 No No 1.37 No No 1 No No 0.275 Yes Yes 0.0276 No No 0.545 No No 1.25 No No 0.0454 Yes No 0.958 No No 1.23 No No 1.76 No No 0.852 No No 0.0564 No No 0.837 No No Considered ROPC? No No No No No No No No No No No No No No Yes No No No Yes No No No Yes No No No No No No PAGE 1 OF 1 ATTACHMENT 1, TABLE 4 Results of Background Statistical Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Central Tendency Comparisons Chemical  2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   2‐Methylnaphthalene   4,4'‐DDD   4,4'‐DDT   Acenaphthylene   Anthracene   Antimony   Arsenic   Barium   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   Beryllium   beta‐BHC   bis(2‐Ethylhexyl) phthalate   Cadmium   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Fluoranthene   Fluorene   Fluoride   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   Manganese   MCPA   Mercury   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Selenium   Silver   2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   2‐Methylnaphthalene   4,4'‐DDD   4,4'‐DDT   Acenaphthylene   Anthracene   Antimony   Arsenic   Barium   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene  EN0317151003RDD  Units  mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   Site  Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   ZoneID  EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   Depth  0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐2 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   Comparison  Test Used  WRS   Gehan   Gehan   Gehan   WRS   Gehan   Gehan   Gehan   WRS   WRS   Gehan   Gehan   Gehan   Gehan   Gehan   WRS   Gehan   Gehan   WRS   WRS   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   WRS   Gehan   WRS   Gehan   Gehan   Gehan   Gehan   Gehan   WRS   WRS   WRS   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   WRS   WRS   Gehan   Gehan   Gehan   Gehan   Statistical Decision   Probability that the  Observed Differences Would  with 0.05 Significance  Level Occur Purely by Chance 0.000 Site > Bkgd  0.001 Site > Bkgd  0.016 Site > Bkgd  0.070 NSD 0.074 NSD 0.006 Site > Bkgd  0.000 Site > Bkgd  0.618 NSD 1.000 NSD 0.991 NSD 0.000 Site > Bkgd  0.000 Site > Bkgd  0.004 Site > Bkgd  0.000 Site > Bkgd  0.222 NSD 0.997 NSD 0.170 NSD 0.920 NSD 0.500 NSD 0.001 Site > Bkgd  0.002 Site > Bkgd  0.023 Site > Bkgd  0.203 NSD 0.191 NSD 0.210 NSD 0.120 NSD 0.005 Site > Bkgd  0.352 NSD 0.764 NSD 0.267 NSD 0.140 NSD 0.000 Site > Bkgd  0.999 NSD 0.121 NSD 0.500 NSD 0.005 Site > Bkgd  0.000 Site > Bkgd  0.050 Site > Bkgd  0.000 Site > Bkgd  0.001 Site > Bkgd  0.500 NSD 0.000 Site > Bkgd  0.090 NSD 0.016 Site > Bkgd  0.001 Site > Bkgd  0.116 NSD 0.259 NSD 0.025 Site > Bkgd  0.000 Site > Bkgd  0.995 NSD 1.000 NSD 1.000 NSD 0.000 Site > Bkgd  0.000 Site > Bkgd  0.008 Site > Bkgd  0.000 Site > Bkgd  Descriptive Site/Bkgd Statistics  Number of   Number of   Number of   Median of   Mean of  Bkgd  Site  Bkgd   Number of  Bkgd   Median of  Mean of  Bkgd   Percent  Site Detects Detects Site Detects Detects Site Detects Samples Samples Detects Site Detects 0.0000107 2.00E‐07 6.40E‐06 2.00E‐07 23 23 147 147 100 0.025 0.00696 0.025 0.0034 2 9 13 148 22 0.00135 0.00108 0.00135 0.00108 2 31 4 148 6 0.00108 0.000161 0.00108 0.000138 2 13 30 146 15 0.00478 0.00162 0.0034 0.00078 9 13 147 148 69 0.00113 0.00123 0.0008 0.00071 3 31 5 148 10 0.0196 0.000773 0.00062 0.000728 7 31 6 148 23 0.763 0.246 0.285 0.224 20 42 260 267 48 13.4 10.3 6.17 9.15 49 52 267 267 94 113 127 111 125 42 42 268 268 100 0.0947 0.00128 0.002 0.001 13 31 13 144 42 0.0645 0.00126 0.00265 0.000895 12 31 28 147 39 0.0639 0.00149 0.0028 0.0011 17 31 107 148 55 0.0218 0.00107 0.00168 0.0009 12 31 19 147 39 0.0887 0.00246 0.0029 0.0019 6 28 46 146 21 0.75 0.883 0.769 0.831 38 40 267 267 95 0.00073 0.00013 0.00073 0.000105 1 13 16 147 8 0.0287 0.0192 0.0287 0.019 1 31 53 141 3 0.227 0.257 0.21 0.242 41 43 267 268 95 0.0838 0.00112 0.0024 0.00089 19 31 135 145 61 0.0268 0.00111 0.00505 0.000895 4 31 8 148 13 0.0377 0.00646 0.0096 0.0064 3 31 6 141 10 0.00055 0.0000771 0.00055 0.000069 1 13 23 147 8 0.00055 0.000171 0.00055 0.000135 1 13 20 148 8 0.0005 0.000156 0.0005 0.00013 1 13 24 147 8 0.000785 0.000212 0.000785 0.000145 2 13 69 145 15 0.171 0.00135 0.0029 0.0012 14 31 112 147 45 0.00795 0.0019 0.00795 0.0021 2 31 17 148 6 1.44 2.41 1.5 1.67 12 21 158 267 57 0.00047 0.0000818 0.00047 0.000072 1 13 50 145 8 1.13 0.621 0.865 0.539 10 19 201 268 53 0.0386 0.00083 0.0019 0.000825 7 31 8 145 23 375 426 347 403 23 23 267 267 100 0.94 0.425 0.94 0.45 1 9 18 148 11 0.0112 0.0155 0.00905 0.0129 16 25 212 260 64 0.00179 0.000175 0.00104 0.00015 4 13 66 144 31 0.00133 0.00135 0.00115 0.001 10 31 27 147 32 0.014 0.000538 0.014 0.00047 2 10 73 268 20 0.0687 0.00116 0.00195 0.00088 14 31 61 148 45 0.199 0.00128 0.004 0.001 13 31 98 147 42 0.199 0.292 0.17 0.268 27 40 266 266 68 0.223 0.0498 0.0568 0.0425 35 43 266 268 81 6.90E‐06 2.00E‐07 4.00E‐07 2.00E‐07 38 40 147 147 95 0.025 0.00696 0.025 0.0034 2 16 13 148 13 0.00388 0.00108 0.00135 0.00108 4 58 4 148 7 0.00108 0.000161 0.00108 0.000138 2 22 30 146 9 0.0044 0.00162 0.00245 0.00078 10 22 147 148 45 0.00113 0.00123 0.0008 0.00071 3 58 5 148 5 0.0118 0.000773 0.000755 0.000728 12 58 6 148 21 0.596 0.246 0.274 0.224 30 76 260 267 39 13.1 10.3 7 9.15 88 92 267 267 96 110 127 109 125 75 75 268 268 100 0.0568 0.00128 0.0017 0.001 22 58 13 144 38 0.0392 0.00126 0.00126 0.000895 20 58 28 147 34 0.0394 0.00149 0.002 0.0011 28 58 107 148 48 0.0166 0.00107 0.0012 0.0009 16 58 19 147 28  Percent  Detects  Bkgd 100 9 3 21 99 3 4 97 100 100 9 19 72 13 32 100 11 38 100 93 5 4 16 14 16 48 76 11 59 34 75 6 100 12 82 46 18 27 41 67 100 99 100 9 3 21 99 3 4 97 100 100 9 19 72 13 Number of Bkgd  UTL Exceedances 15 1 0 2 2 1 3 5 5 0 8 6 8 7 2 0 1 1 4 8 3 2 1 1 1 2 8 1 0 1 2 7 1 1 1 4 2 2 7 8 0 9 18 1 1 2 2 1 6 6 9 1 12 7 9 8 PAGE 1 OF 2 ATTACHMENT 1, TABLE 4 Results of Background Statistical Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Central Tendency Comparisons Chemical  Benzo(k)fluoranthene   Beryllium   beta‐BHC   bis(2‐Ethylhexyl) phthalate   Cadmium   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Fluoranthene   Fluorene   Fluoride   Heptachlor   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   Manganese   MCPA   Mercury   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Selenium   Silver   Silvex  Notes: EEL = Environmental Effect Laboratory ft = feet mg/kg = milligrams per kilogram NSD = no significant difference TEQ = 2,3,7,8‐TCDD toxicity equivalents UTL = upper threshold limit  WRS = Wilcoxon Rank Sum EN0317151003RDD  Units  mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   Site  Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   Group 5/9   ZoneID  EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   EEL   Depth  0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   0‐10 ft   Comparison  Test Used  Gehan   WRS   Gehan   Gehan   WRS   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   WRS   Gehan   WRS   Gehan   Gehan   Gehan   Gehan   Gehan   Gehan   WRS   Gehan   Statistical Decision   Probability that the  Observed Differences Would  with 0.05 Significance  Level Occur Purely by Chance 0.218 NSD 0.989 NSD 0.219 NSD 0.968 NSD 0.500 NSD 0.001 Site > Bkgd  0.013 Site > Bkgd  0.050 NSD 0.250 NSD 0.239 NSD 0.256 NSD 0.170 NSD 0.000 Site > Bkgd  0.583 NSD 0.220 NSD 0.185 NSD 0.306 NSD 0.424 NSD 0.000 Site > Bkgd  1.000 NSD 0.180 NSD 0.500 NSD 0.018 Site > Bkgd  0.000 Site > Bkgd  0.008 Site > Bkgd  0.000 Site > Bkgd  0.000 Site > Bkgd  1.000 NSD 0.004 Site > Bkgd  0.257 NSD Descriptive Site/Bkgd Statistics  Number of   Number of   Number of   Median of   Mean of  Bkgd  Site  Bkgd   Number of  Bkgd   Median of  Mean of  Bkgd   Percent  Site Detects Detects Site Detects Detects Site Detects Samples Samples Detects Site Detects 0.0449 0.00246 0.0012 0.0019 12 54 46 146 22 0.797 0.883 0.774 0.831 69 71 267 267 97 0.00073 0.00013 0.00073 0.000105 1 22 16 147 5 0.0395 0.0192 0.0395 0.019 2 58 53 141 3 0.184 0.257 0.147 0.242 74 76 267 268 97 0.0479 0.00112 0.0022 0.00089 34 58 135 145 59 0.0268 0.00111 0.00505 0.000895 4 58 8 148 7 0.0377 0.00646 0.0096 0.0064 3 58 6 141 5 0.00055 0.0000771 0.00055 0.000069 1 22 23 147 5 0.00055 0.000171 0.00055 0.000135 1 22 20 148 5 0.0005 0.000156 0.0005 0.00013 1 22 24 147 5 0.000785 0.000212 0.000785 0.000145 2 22 69 145 9 0.0938 0.00135 0.0027 0.0012 26 58 112 147 45 0.00795 0.0019 0.00795 0.0021 2 58 17 148 3 2.53 2.41 1.76 1.67 24 38 158 267 63 0.00058 0.000132 0.00058 0.000125 1 22 11 148 5 0.00047 0.0000818 0.00047 0.000072 1 22 50 145 5 1.07 0.621 0.85 0.539 15 29 201 268 52 0.0303 0.00083 0.0014 0.000825 9 58 8 145 16 340 426 315 403 45 45 267 267 100 0.94 0.425 0.94 0.45 1 16 18 148 6 0.0109 0.0155 0.0094 0.0129 27 40 212 260 68 0.00179 0.000175 0.00104 0.00015 4 22 66 144 18 0.00126 0.00135 0.0011 0.001 13 58 27 147 22 0.019 0.000538 0.0146 0.00047 4 19 73 268 21 0.0412 0.00116 0.0017 0.00088 24 58 61 148 41 0.114 0.00128 0.004 0.001 23 58 98 147 40 0.237 0.292 0.182 0.268 36 71 266 266 51 0.172 0.0498 0.0638 0.0425 62 74 266 268 84 0.0014 0.000248 0.0014 0.00021 1 16 37 147 6  Percent  Detects  Bkgd 32 100 11 38 100 93 5 4 16 14 16 48 76 11 59 7 34 75 6 100 12 82 46 18 27 41 67 100 99 25 Number of Bkgd  UTL Exceedances 2 1 1 2 4 13 3 2 1 1 1 2 14 1 2 1 1 4 9 2 1 1 4 2 4 11 13 1 20 1 PAGE 2 OF 2 ATTACHMENT 1, TABLE 5 Aroclor to PCB Congener Extrapolation  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Aroclor 1254 EF Aroclor 1260 EF Mammal TEF Soil Horizon 95%  (ft bgs) Aroclor UCL Convert Aroclor 1254 to Congeners 0‐2  Aroclor 1254  0.04730 0‐10  Aroclor 1254  0.03190 Convert Congeners to TEQs 0‐2 TEQ‐Mammal ‐‐ 0‐10 TEQ‐Mammal ‐‐ Convert Aroclor 1260 to Congeners 0‐2  Aroclor 1260  0‐10  Aroclor 1260  Convert Congeners to TEQs 0‐2 TEQ‐Mammal 0‐10 TEQ‐Mammal 77 1.5E‐02 1.3E‐02 1.0E‐04 105 1.2E‐01 8.2E‐02 3.0E‐05 114 4.5E‐03 1.5E‐03 3.0E‐05 118 2.7E‐01 1.6E‐01 3.0E‐05 PCB Congener 123 126 3.0E‐03 7.5E‐03 2.3E‐03 6.4E‐03 3.0E‐05 1.0E‐01 156 6.3E‐02 5.5E‐02 3.0E‐05 157 1.2E‐02 2.5E‐02 3.0E‐05 167 2.1E‐02 4.3E‐02 3.0E‐05 169 3.7E‐04 6.4E‐04 3.0E‐02 189 3.0E‐03 6.4E‐03 3.0E‐05 Units PCB‐TEQ mg/Kg mg/Kg 7.1E‐04 4.8E‐04 1.4E‐04 9.6E‐05 5.7E‐03 3.8E‐03 2.1E‐04 1.4E‐04 mg/Kg mg/Kg 7.1E‐08 4.8E‐08 4.3E‐08 2.9E‐08 1.7E‐07 1.1E‐07 6.4E‐09 4.3E‐09 0.03790 0.01030 mg/Kg mg/Kg 4.9E‐04 1.3E‐04 8.7E‐05 2.4E‐05 3.1E‐03 8.4E‐04 5.7E‐05 1.5E‐05 ‐‐ ‐‐ mg/Kg mg/Kg 4.9E‐08 1.3E‐08 2.6E‐08 7.1E‐09 9.3E‐08 2.5E‐08 1.7E‐09 4.6E‐10 Notes: EF = extraction factor as defined by SRAM Rev. 2 Addendum (MWH, 2014) ft bgs = feet below ground surface mg/kg = milligrams per kilogram ND = not detected PCB = polychlorinated biphenyl TEF = toxicity equivalency factor TEQ = 2,3,7,8‐TCDD toxicity equivalents UCL = upper confidence limit on the mean EN0317151003RDD 81 3.0E‐03 2.3E‐03 3.0E‐04 Extrapolated Congener Concentration 1.3E‐02 1.4E‐04 3.5E‐04 3.0E‐03 8.6E‐03 9.6E‐05 2.4E‐04 2.0E‐03 TCDD Toxicity Equivalents (PCB‐TEQ) 3.8E‐07 4.3E‐09 3.5E‐05 8.9E‐08 2.6E‐07 2.9E‐09 2.4E‐05 6.0E‐08 Extrapolated Congener Concentration 6.1E‐03 8.7E‐05 2.4E‐04 2.1E‐03 1.6E‐03 2.4E‐05 6.6E‐05 5.7E‐04 TCDD Toxicity Equivalents (PCB‐TEQ) 1.8E‐07 2.6E‐09 2.4E‐05 6.3E‐08 4.9E‐08 7.1E‐10 6.6E‐06 1.7E‐08 5.7E‐04 3.8E‐04 9.9E‐04 6.7E‐04 1.8E‐05 1.2E‐05 1.4E‐04 9.6E‐05 1.7E‐08 1.1E‐08 3.0E‐08 2.0E‐08 5.3E‐07 3.5E‐07 4.3E‐09 2.9E‐09 9.5E‐04 2.6E‐04 1.6E‐03 4.4E‐04 2.4E‐05 6.6E‐06 2.4E‐04 6.6E‐05 2.8E‐08 7.7E‐09 4.9E‐08 1.3E‐08 7.3E‐07 2.0E‐07 7.3E‐09 2.0E‐09 Total PCB‐TEQ 0‐2 ft bgs 0‐10 ft bgs 3.7E‐05 2.5E‐05 2.5E‐05 6.9E‐06 6.2E‐05 3.2E‐05 PAGE 1 OF 1 ATTACHMENT 1, TABLE 6 Risk and Hazard Estimates for Exposure to Soil (0 to 10 feet bgs)  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Analyte  2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   2‐Methylnaphthalene   4,4'‐DDD   4,4'‐DDT   Acenaphthene   Acenaphthylene   Acetone   Anthracene   Antimony   Aroclor‐1254   Aroclor‐1260   Aroclor‐5460   Arsenic   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   beta‐BHC   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Ethylbenzene   Fluoranthene   Fluorene   Fluoride   Heptachlor   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   MCPA   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Silvex   Styrene   Xylenes, Total  Exposure Point  Concentration (mg/kg) 2.49E‐05 2.56E‐02 2.03E‐03 1.80E‐03 4.23E‐03 6.50E‐03 1.95E‐03 1.60E‐02 1.33E‐02 5.20E‐01 3.19E‐02 1.03E‐02 7.06E‐03 1.65E+01 1.14E‐01 7.08E‐02 9.58E‐02 2.33E‐02 5.44E‐02 7.30E‐04 1.91E‐01 6.19E‐03 1.38E‐02 5.50E‐04 5.50E‐04 5.00E‐04 1.10E‐03 3.12E‐04 2.18E‐01 3.33E‐03 2.81E+00 5.80E‐04 4.70E‐04 9.32E‐01 2.69E‐02 9.40E‐01 2.81E‐03 1.53E‐03 1.48E‐03 1.17E‐02 4.88E‐02 2.37E‐01 2.54E‐01 1.40E‐03 5.21E‐04 1.36E‐03 Carcinogenic a RBSL (mg/kg) 4.81E‐06 ‐‐ ‐‐ 2.46E+00 1.74E+00 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.32E‐01 2.32E‐01 2.32E‐01 6.58E‐02 3.87E‐01 3.87E‐02 3.87E‐01 ‐‐ 3.87E‐01 3.94E‐01 3.87E+00 1.13E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2.31E+00 ‐‐ ‐‐ ‐‐ 1.44E‐01 1.07E‐01 1.29E+00 3.87E‐01 ‐‐ 2.97E+00 3.28E‐02 1.46E+01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Soil Contact Exposure Scenario Noncarcinogenic Cancer Risk 5.18E‐06 ‐‐ ‐‐ 7.31E‐10 2.43E‐09 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.37E‐07 4.44E‐08 3.04E‐08 2.51E‐04 2.95E‐07 1.83E‐06 2.48E‐07 ‐‐ 1.41E‐07 1.85E‐09 4.94E‐08 5.46E‐08 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.35E‐10 ‐‐ ‐‐ ‐‐ 4.02E‐09 4.37E‐09 7.20E‐07 6.95E‐08 ‐‐ 9.45E‐10 4.66E‐08 1.01E‐10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3E‐04 Percent Contribution 2.0% ‐‐ ‐‐ 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.1% 0.0% 0.0% 96.6% 0.1% 0.7% 0.1% ‐‐ 0.1% 0.0% 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.3% 0.0% ‐‐ 0.0% 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100.0% RBSLa (mg/kg) 5.05E‐05 5.49E+02 1.62E+02 ‐‐ 3.43E+01 3.23E+03 2.98E+03 6.01E+04 1.64E+04 2.64E+01 1.10E+00 1.10E+00 1.10E+00 2.16E+01 ‐‐ ‐‐ ‐‐ 1.65E+03 ‐‐ ‐‐ ‐‐ ‐‐ 6.11E+02 4.12E+02 4.12E+02 2.06E+01 2.06E+01 2.98E+03 2.20E+03 2.18E+03 3.04E+03 3.43E+01 8.92E‐01 2.34E+02 ‐‐ 3.43E+01 2.90E+02 1.37E+01 6.81E+02 5.33E+01 1.64E+04 1.65E+03 2.30E+02 5.49E+02 1.14E+04 4.28E+02 Hazard Index Hazard Quotient 4.93E‐01 4.66E‐05 1.25E‐05 ‐‐ 1.23E‐04 2.02E‐06 6.55E‐07 2.66E‐07 8.10E‐07 1.97E‐02 2.90E‐02 9.35E‐03 6.41E‐03 7.63E‐01 ‐‐ ‐‐ ‐‐ 1.41E‐05 ‐‐ ‐‐ ‐‐ ‐‐ 2.26E‐05 1.34E‐06 1.34E‐06 2.43E‐05 5.34E‐05 1.05E‐07 9.89E‐05 1.53E‐06 9.23E‐04 1.69E‐05 5.27E‐04 3.98E‐03 ‐‐ 2.74E‐02 9.69E‐06 1.12E‐04 2.17E‐06 2.20E‐04 2.97E‐06 1.43E‐04 1.10E‐03 2.55E‐06 4.58E‐08 3.18E‐06 1 Percent Contribution 36.4% 0.0% 0.0% ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 1.5% 2.1% 0.7% 0.5% 56.3% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.1% 0.0% 0.0% 0.3% ‐‐ 2.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.1% 0.0% 0.0% 0.0% 100.0% Extrapolated PCB Congeners PCB TEQ 3.18E‐05 3.57E‐06 9E‐06 100.0% 3.86E‐05 0.8 100.0% Notes: a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory,  Ventura County California  (MWH, 2014). bgs = below ground surface mg/kg = milligrams per kilogram PCB = polychlorinated biphenyl TEQ = 2,3,7,8‐TCDD toxicity equivalents EEL App_E1_HHRA tables_060815.xlsx 1 of 1 ATTACHMENT 1, TABLE 7 Evaluation of Potential for Hotspots in Soil (0 to 10 feet bgs)  Data Summary and Findings Report, Boeing RFI Subarea 5/9 South, EEL RFI Site Santa Susana Field Laboratory, Ventura County, California Maximum  Concentration (mg/kg) 5.19E‐05 3.20E‐02 1.20E‐02 1.80E‐03 1.90E‐02 1.70E‐02 2.10E‐03 1.60E‐02 1.30E‐01 7.50E+00 9.90E‐02 4.60E‐02 7.06E‐03 1.10E+02 1.20E+00 7.40E‐01 1.00E+00 2.30E‐01 5.20E‐01 7.30E‐04 1.50E+00 9.60E‐02 9.90E‐02 5.50E‐04 5.50E‐04 5.00E‐04 1.10E‐03 3.12E‐04 2.30E+00 1.50E‐02 1.12E+01 5.80E‐04 4.70E‐04 3.20E+00 2.60E‐01 9.40E‐01 2.81E‐03 4.70E‐03 2.20E‐03 4.30E‐02 9.10E‐01 2.50E+00 3.50E+00 1.40E‐03 7.23E‐04 1.36E‐03 Suburban Residential Soil Contact Exposure Scenario Carcinogenic Noncarcinogenic Lowest  10X Lowest RBSLa RBSLa RBSL  RBSL (mg/kg) (mg/kg) (mg/kg) (mg/kg) 4.81E‐06 5.05E‐05 4.81E‐06 4.81E‐05 ‐‐ 5.49E+02 5.49E+02 5.49E+03 ‐‐ 1.62E+02 1.62E+02 1.62E+03 2.46E+00 ‐‐ 2.46E+00 2.46E+01 1.74E+00 3.43E+01 1.74E+00 1.74E+01 ‐‐ 3.23E+03 3.23E+03 3.23E+04 ‐‐ 2.98E+03 2.98E+03 2.98E+04 ‐‐ 6.01E+04 6.01E+04 6.01E+05 ‐‐ 1.64E+04 1.64E+04 1.64E+05 ‐‐ 2.64E+01 2.64E+01 2.64E+02 2.32E‐01 1.10E+00 2.32E‐01 2.32E+00 2.32E‐01 1.10E+00 2.32E‐01 2.32E+00 2.32E‐01 1.10E+00 2.32E‐01 2.32E+00 6.58E‐02 2.16E+01 6.58E‐02 6.58E‐01 3.87E‐01 ‐‐ 3.87E‐01 3.87E+00 3.87E‐02 ‐‐ 3.87E‐02 3.87E‐01 3.87E‐01 ‐‐ 3.87E‐01 3.87E+00 ‐‐ 1.65E+03 1.65E+03 1.65E+04 3.87E‐01 3.87E+00 3.87E‐01 ‐‐ 3.94E‐01 ‐‐ 3.94E‐01 3.94E+00 3.87E+00 ‐‐ 3.87E+00 3.87E+01 1.13E‐01 ‐‐ 1.13E‐01 1.13E+00 ‐‐ 6.11E+02 6.11E+02 6.11E+03 ‐‐ 4.12E+02 4.12E+02 4.12E+03 ‐‐ 4.12E+02 4.12E+02 4.12E+03 ‐‐ 2.06E+01 2.06E+01 2.06E+02 ‐‐ 2.06E+01 2.06E+01 2.06E+02 2.31E+00 2.98E+03 2.31E+00 2.31E+01 ‐‐ 2.20E+03 2.20E+03 2.20E+04 ‐‐ 2.18E+03 2.18E+03 2.18E+04 ‐‐ 3.04E+03 3.04E+03 3.04E+04 1.44E‐01 3.43E+01 1.44E‐01 1.44E+00 1.07E‐01 8.92E‐01 1.07E‐01 1.07E+00 1.29E+00 2.34E+02 1.29E+00 1.29E+01 3.87E‐01 ‐‐ 3.87E‐01 3.87E+00 ‐‐ 3.43E+01 3.43E+01 3.43E+02 2.97E+00 2.90E+02 2.97E+00 2.97E+01 3.28E‐02 1.37E+01 3.28E‐02 3.28E‐01 1.46E+01 6.81E+02 1.46E+01 1.46E+02 ‐‐ 5.33E+01 5.33E+01 5.33E+02 ‐‐ 1.64E+04 1.64E+04 1.64E+05 ‐‐ 1.65E+03 1.65E+03 1.65E+04 ‐‐ 2.30E+02 2.30E+02 2.30E+03 ‐‐ 5.49E+02 5.49E+02 5.49E+03 ‐‐ 1.14E+04 1.14E+04 1.14E+05 ‐‐ 4.28E+02 4.28E+02 4.28E+03 Analyte  2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   2‐Methylnaphthalene   4,4'‐DDD   4,4'‐DDT   Acenaphthene   Acenaphthylene   Acetone   Anthracene   Antimony   Aroclor‐1254   Aroclor‐1260   Aroclor‐5460   Arsenic   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Benzo(k)fluoranthene   beta‐BHC   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Endosulfan sulfate   Endrin   Endrin aldehyde   Ethylbenzene   Fluoranthene   Fluorene   Fluoride   Heptachlor   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   MCPA   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Silvex   Styrene   Xylenes, Total  Notes: a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa  Susana Field Laboratory, Ventura County California  (MWH, 2014). b  Maximum concentration for this chemical of potential concern exceeds 10 times the lowest RBSL. mg/kg = milligrams per kilogram TEQ = 2,3,7,8‐TCDD toxicity equivalents EEL App_E1_HHRA tables_060815.xlsx Potentialb for Hotspot? Yes No No No No No No No No No No No No Yes No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No 1 of 1 Attachment 2 APPENDIX E1 ATTACHMENT 2  Risk-Based Screening Levels for Recently Detected Chemicals and Radionuclides 1.0 Purpose Human health and ecological risk‐based screening levels (RBSLs) for chemicals previously detected in soil at  Boeing RCRA Facility Investigation subareas of the Santa Susana Field Laboratory (SSFL) were derived and  reported in the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field  Laboratory, Ventura County, California (SRAM Rev. 2 Addendum) (MWH, 2014a), and for radionuclides were  derived and reported per e‐mail communication from Mike Bower/Boeing to Roger Paulson/DTSC, dated  January 14, 2015. However, since these RBSLs were derived, additional chemicals and radionuclides have  been identified as present in site media at SSFL. This attachment provides the RBSLs for chemicals and  radionuclides that were recently detected for the first time at SSFL. Additional chemicals and/or  radionuclides identified as detected at other subareas at SSFL (if any) will be addressed in subsequent  reports as needed.  The RBSLs provided herein were derived using the same exposure assumptions and methods as use for  deriving the previous RBSLs for SSFL. Toxicity values for the RBSL calculations were obtained from the  general hierarchy of toxicity information sources described in Section 3.3 of Attachment 1 of Appendix B of  the SRAM Rev. 2 Addendum (MWH, 2014a). The calculation workbooks are provided as separate electronic  files.  2.0 Results Table 1 provides the human health RBSLs for the suburban resident and the recreator, and Table 2 provides  the ecological RBSLs, for the following chemicals:              4,6‐Dinitro‐o‐cresol  Aniline  Aroclor‐1262  Aroclor‐1268  Aroclor‐5460  Benzidine  Cerium  Ethylene glycol  Hexachlorocyclopentadiene  Nitrobenzene  Nitroglycerin  Uranium  Table 3 provides the human health RBSLs for the suburban resident and the recreator for the following  radionuclides in soil:        Curium‐243/244  Curium‐247/248  Plutonium‐244  Strontium‐90  Thorium‐229  Yttrium‐90  EN0331151041RDD Tables List of Tables 1  Human Health Risk‐based Screening Levels for Recently Detected Chemicals in Soil  2  Ecological Risk‐based Screening Levels for Recently Detected Chemicals in Environmental Media  3  Human Health Risk‐based Screening Levels for Recently Detected Radionuclides in Soil  EN0331151041RDD TABLE 1 Human Health Risk‐based Screening Levels for Recently Detected Chemicals in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California RME Suburban Residential Soil RBSL b Composite Resident Child Chemical   4,6‐Dinitro‐o‐cresol CAS # 534521 Aniline 62533 Aroclor 1262 37324235 Aroclor 1268 11100144 Aroclor 5460 11126424 Benzidine 92875 Cerium 7440451 Ethylene glycol 107211 Hexachlorocyclopentadiene 77474 Nitrobenzene 98953 Nitroglycerin 55630 Uranium 7440611 Notes: '‐"  none established/not applicable. HQ ‐ hazard quotient mg/kg ‐ milligrams per kilogram RBSL ‐ Risk‐based Screening Level RME ‐ reasonable maximum exposure RME SRAM‐based Suburban Residential Garden RBSL c Composite Resident Child Cancer (10‐6) Noncancer (HQ=1) Lowest Cancer (10 ) Noncancer (HQ=1) Lowest Cancer (10 ) Noncancer (HQ=1) Lowest (mg/kg) ‐ (mg/kg) 6.11E+00 (mg/kg) 6.11E+00 (mg/kg) ‐ (mg/kg) 1.33E‐02 (mg/kg) 1.33E‐02 (mg/kg) ‐ (mg/kg) 2.85E+01 (mg/kg) 2.85E+01 ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ 9.13E+01 2.32E‐01 2.32E‐01 2.32E‐01 1.04E‐03 ‐ ‐ ‐ 3.26E+00 3.06E+01 ‐ 4.28E+02 1.10E+00 1.10E+00 1.10E+00 1.83E+02 1.28E+06 1.22E+05 3.66E+02 1.17E+02 6.11E+00 2.27E+02 9.13E+01 2.32E‐01 2.32E‐01 2.32E‐01 1.04E‐03 1.28E+06 1.22E+05 3.66E+02 3.26E+00 6.11E+00 2.27E+02 1.74E‐02 4.88E‐04 4.88E‐04 4.88E‐04 3.28E‐07 ‐ ‐ ‐ ‐ 1.31E‐02 ‐ 2.56E‐01 7.21E‐03 7.21E‐03 7.21E‐03 1.82E‐01 ‐ 3.95E+00 2.10E+00 2.06E‐01 8.21E‐03 1.08E+00 1.74E‐02 4.88E‐04 4.88E‐04 4.88E‐04 3.28E‐07 ‐ 3.95E+00 2.10E+00 2.06E‐01 8.21E‐03 1.08E+00 2.52E+02 5.64E‐01 5.64E‐01 5.64E‐01 2.87E‐03 ‐ ‐ ‐ 4.56E+01 8.45E+01 ‐ 2.00E+03 5.14E+00 5.14E+00 5.14E+00 8.55E+02 1.79E+07 5.70E+05 1.71E+03 6.57E+02 2.85E+01 1.06E+03 2.52E+02 5.64E‐01 5.64E‐01 5.64E‐01 2.87E‐03 1.79E+07 5.70E+05 1.71E+03 4.56E+01 2.85E+01 1.06E+03  Please note that different chemical names have been used for different programs at the SSFL, and there can be additional analyte synonyms than those presented. Therefore, any chemical synonym should be verified using the CAS number listed.    b c  Suburban Residential and Recreational Soil RBSLs include the following pathways:  ingestion of soil, dermal contact with soil, and inhalation of dust and volatiles from soil.  SRAM‐based Suburban Residential Garden RBSLs include the ingestion of fruits/vegetables pathway. ‐6 RME Recreational Soil RBSL b Child Chemical Synonym a 4,6‐Dinitro‐2‐Methylphenol a ‐6 Composite Recreator TABLE 2 Ecological Risk‐based Screening Levels for Recently Detected Chemicals in Environmental Media RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Water Chemical   4,6‐Dinitro‐o‐cresol Aniline Aroclor 1262 Aroclor 1268 Aroclor 5460 Benzidine Cerium Ethylene Glycol Hexachlorocyclopentadiene Nitrobenzene Nitroglycerin Uranium CAS # Chemical Synonym 534521 62533 37324235 11100144 11126424 92875 7440451 107211 77474 98953 55630 7440611 4,6‐Dinitro‐2‐Methylphenol ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ ‐ Water  Column  Terrestrial  Community Plants RBSLa RBSLa (mg/L) (mg/L) NC NC NC NC NC NC NC NC NC 8 NC NC 0.23 NC NC NC NC 0.0039 NC NC 0.0052 27 NC NC Sediment Lowest Low TRV‐ High TRV‐ Based  Based  RBSLa,b RBSLa,b (mg/L) (mg/L) 18 NC NC NC NC 3.6 NC NC 20 6.1 NC NC NTV NC NC NC NC 18 NC NC 37 10 NC NC Lowest Low TRV‐ High TRV‐ Based  Based  RBSLa,b RBSLa,b (mg/kg) (mg/kg) NC NC NC NC NC NC NC NC NC 0.021 NTV NC NC NC NC NC NC NC NC NC NC NTV NTV NC Soil Terrestrial  Plants RBSLa (mg/L) Soil  Invertebrates RBSLa (mg/kg) 20 NTV 40 40 40 NTV NTV 960 10 NTV NTV 5 NTV NTV 500 500 500 NTV NTV 960 NTV 40 NTV 23 Soil Vapor Lowest Low TRV‐ High TRV‐ Based  Based  RBSLa,b RBSLa,b (mg/kg) (mg/kg) 7.4 25 0.039 0.039 0.039 2.5 NTV 920 3.0 4.1 14 28 NTV 250 0.39 0.39 0.39 12 NTV 4,610 5.6 6.9 150 55 Low TRV‐ Based RBSLa (mg/m3) High TRV‐ Based RBSLa (mg/m3) NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA Notes: a  Calculated with a target hazard quotient of 1.  EcoRBSLs for surface water, soil invertebrates, sediment, and terrestrial plants are equivalent to their respective medium‐specific benchmarks; therefore, these EcoRBSLs were reported in the same  number of significant figures as the source documents from which the benchmarks were selected.  Avian and mammalian EcoRBSLs are calculated rather than derived from published values; therefore, EcoRBSLs with values less than 1,000 were  reported using two significant figures and values greater than 1,000 were reported using three significant figures. b  Lowest Low and lowest High TRV‐based RBSLs for water and soil are selected from the EcoRBSLs for upper trophic level receptors.  Lowest Low and lowest High sediment RBSLs are selected as the lower of the sediment benthic community and  the great blue heron sediment EcoRBSLs. ‐‐ Not available, or could not be located High TRV ‐ mid level effect toxicity reference value Low TRV ‐ no effect toxicity reference value mg/kg ‐ milligrams per kilogram mg/m3 ‐ milligrams per cubic meter mg/L ‐ milligrams per liter NA ‐ not applicable NC ‐ not calculated NTV ‐ no toxicity value RBSL ‐ risk‐based screening level TABLE 3 Human Health Risk‐based Screening Levels for Recently Detected Radionuclides in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Radionuclidea Curium‐243/244 Curium‐247/248 Plutonium‐244 Strontium‐90 Thorium‐229 Yttrium‐90 a Synonym Cm‐243/244 Cm‐247/248 Pu‐244+D Sr‐90+D Th‐229+D Y‐90m Soil Ingestion RBSL (pCi/g) 6.27E+00 9.37E‐01 2.87E+00 8.23E+00 1.27E+00 1.63E+07 Suburban Residential Soil RBSL Total Soil Produce Soil Soil External RBSL without  Produce  Consumption Inhalation Exposure Consumption RBSL RBSL RBSL (pCi/g) (pCi/g) (pCi/g) (pCi/g)b 2.73E+02 3.34E‐01 3.17E‐01 6.95E‐03 4.99E+01 1.53E‐02 1.50E‐02 1.03E‐03 1.38E+02 6.36E‐02 6.22E‐02 3.11E‐03 2.33E+04 7.22E+00 3.85E+00 6.65E‐03 3.58E+01 4.37E‐01 3.22E‐01 1.38E‐03 8.54E+11 2.20E+03 2.20E+03 2.31E+04 Recreator Soil RBSL Soil Ingestion RBSL (pCi/g) 2.93E+01 4.37E+00 1.34E+01 3.84E+01 5.93E+00 7.59E+07 Soil Inhalation RBSL (pCi/g) 3.83E+03 6.99E+02 1.93E+03 3.27E+05 5.02E+02 1.20E+13 Soil External Exposure RBSL (pCi/g) 1.62E+00 7.44E‐02 3.09E‐01 3.50E+01 2.12E+00 1.07E+04 Total Soil RBSL (pCi/g) 1.53E+00 7.31E‐02 3.02E‐01 1.83E+01 1.56E+00 1.07E+04  RBSLs calculated for curium‐243 and curium‐248 are used for curium‐243/244 and curium‐247/248, respectively, because they are the most conservative of the isotope pair. b  Total Soil RBSLs without Consumption of Produce were calculated as follows:       [1/(1/Soil Ingestion RBSL+1/Soil Inhalation RBSL+1/Soil External Exposure RBSL)] "‐" ‐ not applicable pCi/g ‐ picocuries per gram RBSL ‐ risk‐based screening level Appendix E2 ERA APPENDIX E2  Ecological Risk Assessment for the Environmental Effects Laboratory RFI Site 1.0 Introduction This appendix provides the results of the ecological risk assessment (ERA) for the Environmental Effects  Laboratory (EEL) Resource Conservation and Recovery Act facility investigation (RFI) site (the portion of the  site located within Administrative Area III only) in Boeing RFI Subarea 5/9 South at the Santa Susana Field  Laboratory (SSFL) in Ventura County, California. The objective of this ERA is to determine whether exposure  to environmental media at the site could pose unacceptable risks to ecological receptors and may require  evaluation of corrective action as part of a corrective measure study (CMS), or whether estimated risks are  acceptable and the site, or portions thereof, are eligible for a No Further Action (NFA) designation. Appendix  E1 provides the results of the human health risk assessment (HHRA) and Appendix E3 provides the results of  the non‐CMS area evaluations for human health and ecological receptors for the EEL RFI site. Additional data  were collected by the United States Department of Energy (DOE) and provided to Boeing after preparation  of the EEL DSFR had commenced; these data were not included in the risk assessments presented in  Appendices E1 through E3 and are evaluated in a qualitative nature only in Appendix E4.  This ERA was performed following the methods and assumptions described in the Final Standardized Risk  Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory, Ventura County, California  (SRAM Rev. 2 Addendum) (MWH, 2014) and the Integration of the Surficial Media Operable Unit Risk  Assessment Methodology and the Data Quality Objectives Process, Boeing RCRA Facility Investigation, Santa  Susana Field Laboratory, Ventura County, California (CH2M HILL, 2013a), which was submitted as  Appendix C of the Comprehensive Data Quality Objectives Report. Chemical and radiological sampling  results for environmental media at the EEL RFI site were used to estimate potential risks and hazards to  ecological receptors and to identify risk drivers contributing to unacceptable risks and hazards, if any.  1.1 Background 1.2 Assumptions The EEL RFI site is located on the boundary between Administrative Areas III and IV in the western portion of  the SSFL (refer to Figure 1‐1 of this EEL RFI site Data Summary and Findings Report [EEL DSFR]). The site is  currently inactive, and all structures have been demolished. A summary of the site history and existing  conditions is provided in Section 2 of this EEL DSFR. Additional detailed information on the historical use and  site conditions at the EEL RFI site are presented in the Group 5 – Central Portions of Areas III and IV RCRA  Facility Investigation Report, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2008)  and the Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI Subarea 5/9  South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California (CH2M HILL, 2013b).  This ERA for the EEL RFI site is based on the following assumptions and constraints, which are typical for  ERAs currently being performed:   Evaluations of current exposures are based on existing conditions.   Future land use is assumed to revert to native conditions.   The abiotic media of primary ecological concern include soil and soil vapor.   Current chemical concentrations are present at a steady state and will not change over time.   Chemicals not analyzed for are not considered present or evaluated, although they may be indicated as  uncertainties in the ERA.  EN0411151012BAO 1 APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE  Chemicals with sample quantitation limits (SQLs) exceeding the most conservative screening criteria are  retained for further evaluation in the ERA but are not used for CMS recommendations.   Home ranges of representative species are considered in the estimation of potential risk.   Potential ecological risks are evaluated and presented in this ERA for terrestrial plants, terrestrial soil  invertebrates, the deer mouse, and the hermit thrush; potential risks to large‐home‐range (LHR)  receptors (that is, the mule deer, bobcat, red‐tail hawk, and great blue heron) will be evaluated on a  subarea‐wide and facility‐wide basis and presented under separate cover in the LHR ERA.    1.3 Organization This ERA includes the following components:   Chemical Risk Evaluation (Section 2.0). This section presents a description of the ecological setting,  exposure pathway analyses, and identification of CPECs (problem formulation); identification of  exposure scenarios, calculation of exposure point concentrations, and presentation of the EcoRBSLs  (analyses); and estimation of potential risks and evaluation the lines of evidence to identify COECs (risk  characterization).    Radiological Risk Evaluation (Section 3.0). This section presents identification of radionuclides of  potential ecological concern, evaluation of potential exposure, and estimation of potential risks to  ecological receptors from radionuclides.    Summary of Ecological Risk Assessment (Section 4.0). This section presents a summary of the  conclusion of the ERA for the EEL RFI site.   Uncertainty Analysis (Section 5.0). This section presents a summary of the uncertainties associated with  the ERA for the EEL RFI site.    Identification of CMS and NFA Areas (Section 6.0). This section presents the verification that acceptable  risks to ecological receptors are expected from potential exposure to soil and soil vapor at the EEL RFI  site for the portions of the site outside the recommended CMS areas.    References (Section 7.0). The references used to prepare this ERA are listed in this section.   Attachment 1. Supporting tables to the ERA are presented in this attachment.  2.0 Chemical Risk Evaluation 2.1 Problem Formulation 2.1.1 Ecological Setting The chemical risk evaluation presents an analysis of potential adverse effects from chemical releases at the  EEL RFI site including inorganic and/or organic constituents. The evaluation was completed following the  SRAM Rev. 2 Addendum (MWH, 2014).  The problem formulation contains the background information on the site and/or exposure area used to  focus the analysis phase of the ERA. It includes a description of the ecological setting, evaluates potential  exposure pathways and routes, and identifies CPECs for the media of potential concern at the site.   Habitat at the EEL RFI site and in the surrounding buffer is generally open, with ruderal vegetation  predominating. There is a small area of scrub/shrub along the western edge of the buffer area. Structures at  the site have been demolished and removed. Dominant plants include red‐stemmed filaree (Erodium  cicutarium), short‐pod mustard (Hirschfeldia incana), red brome (Bromus madritensis), red willow (Salix  laevigata), and mulefat (Baccharis salicifolia). During the reconnaissance‐level site survey conducted in  2008, evidence of plant stress was observed in portions of the site. Several factors could be involved in  causing plant stress, including use of herbicides for vegetation control, previous site activities, and other  causes. Wildlife species (or signs of their presence) observed at the site during the reconnaissance‐level  2 EN0411151012BAO APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE survey included western fence lizard (Sceloporus occidentalis), house finch (Haemorhous mexicanus), Say’s  phoebe (Sayornis saya), California towhee (Melozone crissalis), and gophers (Geomyidae) (burrows).   2.1.2 Exposure Pathway Analysis Exposure pathways refer to the media and routes through which chemical stressors could reach ecological  receptors. Potential exposure pathways must meet specific criteria for an exposure to occur. Aside from  necessary habitat for ecological receptors, a complete exposure pathway must include the following  elements:       Contaminant source (for example, upgradient RFI sites, spills, debris areas)  Mechanism for contaminant release and transport (for example, surface runoff)  Exposure point (for example, soil)  Feasible route of exposure (for example, ingestion)  Receptor (for example, bird, mammal)  The ecological conceptual site model (EcoCSM) identifies exposures that may result under reasonably  anticipated uses of the site under both current and future conditions. Figure E2‐1 depicts the EcoCSM for  the EEL RFI site based on the generalized CSM in the SRAM Rev. 2 Addendum (MWH, 2014). Media of  potential concern and the respective representative species used for in the evaluation are summarized in  Table E2‐1.   2.1.3 Chemicals of Potential Ecological Concern CPECs for this ERA were identified from existing soil and soil vapor data that were evaluated according to  the SRAM Rev. 2 Addendum (MWH, 2014).   2.1.3.1 Data Evaluation and Selection Criteria  The analytical data for the EEL RFI site consisted of chemical concentrations in soil and soil vapor. The depth  to groundwater exceeded typical ecological exposures; therefore, groundwater was not evaluated in this  ERA. A summary of the data for each media is presented in Section 4 of this EEL DSFR.  Data were evaluated in accordance with the processes outlined in the SRAM Rev. 2 Addendum (MWH, 2014)  to identify a set of data of acceptable quality for this ERA. Additional criteria used to generate the final risk  assessment data set include:    Estimated values (flagged with a “J” qualifier) were treated as detected concentrations.    Where field duplicates were collected, the maximum between the duplicate and the original sample was  selected. If there was one detection and one nondetection in the duplicate pair, the detected value was  selected. If both values were nondetect, the lower SQL was selected.   Soil samples retained for evaluation were those collected from 0 to 6 feet below ground surface (bgs),  based on end depth. Data were segregated into depth intervals corresponding to exposure depths for  ecological receptors, as designated in the SRAM Rev. 2 Addendum (MWH, 2014).    Soil vapor samples retained for evaluation were collected from 0 to 6 feet bgs (based on sample  collection end depth).    Soil and soil vapor samples collected from depths greater than 6 feet bgs were excluded because they  are beyond the typical exposure range for ecological receptors.   Table 1 in Attachment 1 to this appendix presents a list of chemicals evaluated at the EEL RFI site and their  respective Chemical Abstract Service numbers. Table 2 in Attachment 1 presents a summary of soil and soil  vapor samples used in the ERA, along with an indication of the representative species for which the sample  falls within its potential exposure range. Table 3 in Attachment 1 presents the chemicals detected in each  medium and depth interval evaluated in this ERA, and Table 4 in Attachment 1 presents summary statistics.   EN0411151012BAO 3 APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE 2.1.3.2 Identification of CPECs  CPECs were identified as all chemicals detected in soil and/or soil vapor meeting the following criteria:   A chemical is detected at the site using validated laboratory analyses.    Chemicals are present in excess of background (where background information is available). The  background evaluation consisted of the following:   If the maximum detection was below the background threshold value (BTV; 95/95 upper threshold  limit [UTL] for soil1), then that chemical was not a CPEC.   If the maximum detection was above the background comparison value, a more rigorous statistical  evaluation was conducted to determine whether the population of site data was statistically  different than the background population, as described in Section 3.3 of the SRAM Rev. 2 Addendum  (MWH, 2014). If the chemical was considered outside of the background population, it was retained  as a CPEC. Results of the statistical evaluation are presented in Table 5 in Attachment 1.   Chemicals for which the maximum detection exceeded two times the soil background comparison value  were retained as a CPEC, regardless of the outcome of the statistical background evaluation (for  example, if a chemical was not determined to be statistically different from the background population,  but the maximum detection exceeded two times the BTV, it was retained as a CPEC).   SQLs of chemicals that were never detected at the EEL RFI site were compared to the most conservative  Low EcoRBSL (refer to Section 2.2.3), as shown in Table 6 in Attachment 1. If the mean SQL exceeded the  minimum Low EcoRBSL and there were detections of other chemicals in that chemical class, the  chemical was retained as a CPEC with the exception of the following:   If the exceedance is based on a single sample and there was no known or suspected site use, then  the chemical was not retained.    If a chemical cannot be analyzed at a SQL equivalent to, or lower than, the Low EcoRBSL for a  nondetect chemical, then it may be appropriate to exclude the chemical as a CPEC. Other  information, including site history and attribution, as well as whether or not the chemical was  detected in other site media, should be considered before excluding such chemical as a CPEC.  The selection of CPECs is shown on Table E2‐2. Nondetect chemicals retained as CPECs as part of the SQL  screen are italicized in all remaining tables.  2.2 Analysis 2.2.1 Exposure Characterization The analysis phase links the problem formulation (Section 2.1 of this appendix) with the risk characterization  (Section 2.3 of this appendix) and consists of the technical evaluation of ecological and chemical data to  determine potential for ecological exposure and effects. The analysis phase includes exposure  characterization and ecological effects characterization. These two components are used to evaluate the  relationships among receptors, potential exposures, and potential effects. The results provide the  information necessary to estimate potential risks to the representative species under the conditions defined  for each exposure area.  The exposure characterization is used to evaluate the relationship between ecological receptors at or near  the site and potential stressors (that is, CPECs). Media and receptors of potential ecological concern were  identified as part of the EcoCSM, as discussed in Section 2.1.2 of this appendix.                                                                 1 Based on data from the Final Chemical Soil Background Study Report (California Environmental Protection Agency, Department of Toxic Substances  Control, 2012).  4 EN0411151012BAO APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE 2.2.1.1 Exposure Scenarios  Exposure scenarios and receptor exposure factors for the SSFL were evaluated and presented in Appendix C  of the SRAM Rev. 2 Addendum (MWH, 2014). The potential exposure scenarios evaluated for the EEL RFI site  are summarized below:   Terrestrial Plants: Potential root uptake from soils (0 to 2 feet bgs). Per the SRAM Addendum Rev. 2  (MWH, 2014), the results will not be used as the sole determination for CMS recommendations.    Soil Invertebrates: Potential ingestion and direct contact with soils (0 to 2 feet bgs). Per the SRAM  Addendum Rev. 2 (MWH, 2014), the results will not be used as the sole determination for CMS  recommendations.   Birds: Potential exposure for birds (hermit thrush) includes incidental ingestion of soil (0 to 2 feet bgs)  and food chain uptake (ingestion of food sources that may have bioaccumulated CPECs).    Mammals: Potential exposure for small mammals (deer mouse) include the following:   Soil: Exposure via incidental ingestion of soil and food chain uptake (ingestion of food sources that  may have bioaccumulated CPECs). The soil depth interval with the maximum potential risk is used  and can include 0 to 2 feet bgs, 0 to 4 feet bgs, or 0 to 6 feet bgs.    Soil Vapor: Exposure through inhalation of soil vapor for burrowing mammals (deer mouse) is  evaluated for CPECs in soil vapor (0 to 6 feet bgs).  2.2.1.2 Exposure Point Concentrations  Exposure point concentrations (EPCs) are calculated from concentrations directly measured in soil and soil  vapor samples collected during field investigations at the EEL RFI site. EPCs were computed using the  methods described in the SRAM Rev. 2 Addendum and represent the 95 percent upper confidence limit on  the mean concentration as a conservative upper‐bound estimate that is not likely to underestimate the  mean concentration.  Polychlorinated biphenyl (PCB) congeners were not evaluated at the SSFL. Concentrations of the dioxin‐like  PCB congeners in soil were estimated based on detected Aroclor‐1254 and ‐1260 concentrations, using the  extrapolation factor approach as described in the SRAM Rev. 2 Addendum (MWH, 2014). From this, the total  2,3,7,8‐TCDD toxicity equivalents (TEQs) were estimated. The extrapolation calculations are provided in  Table 7 in Attachment 1.  The soil interval to be used for estimating risks to burrowing mammals was identified in accordance with the  SRAM Rev. 2 Addendum. The soil interval (0 to 2 feet bgs, 0 to 4 feet bgs, or 0 to 6 feet bgs) resulting in the  highest possible risk and/or hazard estimates was selected as follows: the maximum detected  concentrations of CPECs in each interval were divided by the deer mouse Low EcoRBSL and then summed as  shown in Table 8 in Attachment 1. The 0‐to‐6‐foot‐bgs depth interval for the EEL RFI site resulted in the  highest sum and was used for estimating EPCs for burrowing mammals.   EPCs for CPECs in soil (0 to 2 feet bgs and 0 to 6 feet bgs) are summarized in Table E2‐3. EPCs for CPECs in  soil vapor are (0 to 6 feet bgs) summarized in Table E2‐4.  2.2.1.3 Area Use Factors  Area use factors (AUFs) are used to modify the risk estimates based on how much time the receptor might  actually spend in each exposure area. The AUF is a ratio of the size of the exposure area relative to an  animal’s foraging range. The AUF is set to 1 for the small‐home‐range receptors being evaluated in the RFI  site‐level ERAs (that is, the representative species is considered to spend 100 percent of its time within the  exposure area).    EN0411151012BAO 5 APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE 2.2.2 Ecological Effects Characterization The ecological effects characterization consists of an evaluation of available toxicity or other effects  information that can be used to relate the exposure estimates to a level of adverse effects. This evaluation  was completed for chemicals detected at the SSFL and is presented in Appendix D (Ecological Effects  Characterization Updates) and Appendix E (Inhalation Toxicity Reference Value Updates) of the SRAM Rev. 2  Addendum (MWH, 2014).  2.2.3 Ecological Risk-based Screening Levels EcoRBSLs are media/chemical/receptor‐specific values that were developed from the updated exposure and  toxicity assumptions as documented in a series of technical memoranda included as attachments to the  SRAM Rev. 2 Addendum (MWH, 2014) including:   SRAM Rev. 2 Addendum, Appendix C: Ecological Exposure Assessment Updates for Use in Ecological Risk  Assessments   SRAM Rev. 2 Addendum, Appendix D: Ecological Effects Characterization for Chemicals for Use in  Ecological Risk Assessments   SRAM Rev. 2 Addendum, Appendix E: Inhalation Toxicity Reference Value Updates for Use in Ecological  Risk Assessments   SRAM Rev. 2 Addendum, Appendix F: Ecological Risk‐based Screening Levels for Use in Ecological Risk  Assessments  EcoRBSLs for terrestrial plants and soil invertebrates are equivalent to their respective medium‐specific  benchmarks that represent effect levels, values adjusted to a “no effect” level, as well as reported “no  effect” levels. As a result, a single set of EcoRBSLs was developed for each group.   EcoRBSLs for birds and mammals are back‐calculated from receptor‐specific exposure assumptions and  chemical‐specific toxicity reference values. Low EcoRBSLs are conservative and are mostly based on  no‐observed‐adverse‐effect levels (NOAELs). High EcoRBSLs are based on mid‐level effects or low‐observed‐ adverse‐effect levels (LOAELs).    2.3 Risk Characterization The ecological risk characterization evaluates the evidence linking exposures to CPECs with their potential  ecological effects on the representative species identified for the individual exposure areas (watersheds).  The risk characterization includes risk estimation and risk description, which are used together to identify  chemicals of ecological concern (COECs) for CMS recommendations.     Potential ecological risks are calculated using the sum of fractions approach, as described in the SRAM Rev. 2  Addendum (MWH, 2014) for ecological receptors. Hazard quotients (HQs) are calculated on a  media/chemical/receptor‐specific basis by dividing the EPC by the respective EcoRBSLs to derive a HQ.  Unlike the HHRA, estimated risks are only summed into a hazard index (HI) for those chemicals within  chemical classes exhibiting similar toxic mechanisms (specifically, Aroclors, dioxin/furans, organochlorine  pesticides, low‐molecular‐weight polycyclic aromatic hydrocarbons, high‐molecular‐weight polycyclic  aromatic hydrocarbons, and PCBs). HQs were not summed across exposure pathways (for example  ingestion‐based HQs were not summed with inhalation‐based HQs). Both Low and High EcoRBSLs were used  to provide a range of risk estimates.   Potential risks attributable to background levels in soil are addressed in this ERA by computing incremental  site risks as described in Appendix I of the SRAM Rev. 2 Addendum (MWH, 2014). Incremental risk is defined  as the portion of the site risk in excess of risks that may result from exposure to normal regional  background/ambient concentrations of chemicals found in soil at the EEL RFI site and is presumably  attributable to site‐related releases. Incremental risks were estimated to account for levels associated with  6 EN0411151012BAO APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE background and to provide more information for risk management decisions, including CMS or NFA  recommendations.  2.3.1 Soil Exposure Pathways Potential risks from CPECs in soil were evaluated for exposures by terrestrial plants (root uptake), soil  invertebrates (direct contact, ingestion), and birds and mammals (incidental ingestion and food‐chain  uptake). Receptor‐specific risk estimates, including HQs and HIs (where applicable), are presented in Tables  E2‐5 through E2‐8. A summary of all HQs and chemical group HIs for soil exposures is presented in Table 9 in  Attachment 1.   CPECs with HQs exceeding 1 at the Low EcoRBSL for at least one receptor are summarized below. Those with  HQs exceeding 1 at the High EcoRBSL are indicated in bold. Results are for measured data unless otherwise  indicated (that is, “extrapolated” PCB TEQs and “SQL” for nondetect chemicals retained as CPECs).   Terrestrial plants: none   Soil invertebrates: hexavalent chromium   Hermit thrush: dioxins and furans TEQ for birds, 4,4’‐DDT, PCB TEQ for birds (extrapolated)   Deer mouse: antimony, arsenic, Aroclor‐1248 (SQL), dioxins and furans TEQ for mammals, 2‐methyl‐4‐ chlorophenoxyacetic acid (MCPA), PCB TEQ for mammals (extrapolated)  Chemical group HIs were calculated for birds (Table E2‐7) and mammals (Table E2‐8) for aroclors, PAHs (high  and low), and organochlorine pesticides. The HQ and HI for dioxins and furans TEQ are the same value  because the TEQ is already a summation of dioxin and furan congeners. Note: extrapolated data (PCB TEQs)  and nondetects (SQL‐based CPECs) were not included in the HI calculations. HIs exceeded 1 for the following  (those exceeding 1 at the High EcoRBSL are indicated in bold):    Hermit thrush: aroclors, dioxins and furans TEQ forbirds, and organochlorine pesticides   Deer mouse: dioxins and furans TEQ for mammals  Incremental risks were calculated for the CPECs with site HQs exceeding 1 (listed above) where background  data were available and are presented in Table E2‐9. CPECs with incremental HQs exceeding 1 are  summarized below with those exceeding at the High EcoRBSL noted in bold:   Terrestrial plants: none   Soil invertebrates: none   Hermit thrush: PCB TEQ for birds (extrapolated)   Deer mouse: antimony, arsenic, dioxins and furans TEQ for mammals, MCPA, PCB TEQ for mammals  (extrapolated). A background BTV was not available to calculate incremental risks for Aroclor‐1248.   2.3.2 Soil Vapor Exposure Pathways Potential risks from CPECs in soil vapor were evaluated for inhalation exposures by burrowing mammals and  are presented in Table E2‐10. Trichloroethene had an HQ exceeding 1 at the Low EcoRBSL.  2.3.3 Hot Spot Analysis An additional evaluation was conducted to determine the potential for localized areas where higher  constituent concentrations (that is, potential hot spots) could occur. The soil hot spot evaluation was  conducted using the approach outlined in Appendix J of the SRAM Rev. 2 Addendum (MWH, 2014). To  identify hot spots, maximum detected concentrations of CPECs in soils 0 to 6 feet bgs were compared with  10 times the High EcoRBSL for the most sensitive receptor and are presented in Table 10 in Attachment 1.  The maximum detected concentration of dioxins and furans TEQ for mammals exceeded 10 times the High  EcoRBSL for the most sensitive receptor and may indicate potential hot spots.   EN0411151012BAO 7 APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE 2.3.4 Weight-of-evidence Evaluation The weight of evidence evaluation for chemical constituents is presented in Table E2‐11. CPECs with HQs  exceeding 1 at either the Low or High EcoRBSLs are listed along with their respective incremental risk HQs,  chemical group HIs, and weight‐of‐evidence for retention/exclusion as a COEC. COECs were identified for  CMS recommendations if they met the following weight‐of‐evidence criteria:   Site and incremental HQs (where background values were available) exceeded 1 at the High EcoRBSL  and remaining weight‐of‐evidence indicates that the CPEC poses a potential risk to ecological receptors.    Risk estimates for terrestrial plants and soil invertebrates were not used as the sole determinant for  CMS recommendation (that is, CPECs with HQs>1 for plants or invertebrates, but for no other receptors,  were not retained as COECs).    Risk estimates were calculated using detected results. CPECs retained on the basis of the SQL screen  were not retained for CMS recommendations. EcoRBSLs are a calculated value and are often lower than  achievable for the analytical method or instrument.    Extrapolated results (PCB TEQs) were not retained as COECs. Extrapolated concentrations can exceed  measured concentrations for dioxins and furans TEQs by up to two orders of magnitude. These results  are considered an overestimation of potential concentrations of dioxin‐like PCBs. Results from  extrapolated data are not considered valid for use in determining CMS recommendations. Rather,  measured dioxins and furans TEQ and aroclors results are used.   CPECs identified as potential hot spots. These may include those chemicals already identified as COECs  or may be new chemicals (that is, identified during the hot‐spot screen because all detected results  were screened).  2.3.4.1 Soil Exposure Pathways  Dioxins and furans TEQ for mammals was the only COEC identified for the EEL RFI site. Remaining CPECs  with HQs exceeding 1 were not retained as COECs based on weight‐of‐evidence, as discussed below:   Antimony, arsenic, hexavalent chromium, MCPA, and 4,4’‐DDT were not retained as COECs. Incremental  risk HQs did not exceed 1 at the High EcoRBSL, and no potential hot spots were identified.   Dioxins and furans TEQ for birds was not retained as a COEC. Site and incremental risk HQs did not  exceed 1 at the High EcoRBSL, and potential hot spots were not identified. Dioxins and furans TEQ was  retained as a COEC for mammals as noted above. Toxicity to birds differs from mammals, and it is not  uncommon to show unacceptable risks to one group and not the other.    Aroclor‐1248 was not retained as a COEC. This analyte was identified as a CPEC as a result of the SQL  screen (Table 6 in Attachment 1). Other detected Aroclors did not show unacceptable risks to ecological  receptors. Potential for risks from Aroclor‐1248 were considered low.   PCB TEQs (birds and mammals) were not retained as COECs. This constituent was extrapolated from  Aroclor‐1254 and ‐1260 results. As noted above, dioxins and furans TEQ for mammals was retained as a  COEC. There were no unacceptable risks to ecological receptors from aroclors.  2.3.4.2 Soil Vapor Pathways  No chemicals were retained as COECs. Trichloroethene had site HQs exceeding the Low EcoRBSL but not the  High EcoRBSL.  2.4 Chemical Ecological Risk Conclusions The COECs identified for the EEL RFI site are as follows:    8 Soil COECs: dioxins and furans TEQ for mammals  Soil vapor COECs: none  EN0411151012BAO APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE 3.0 Radionuclide Risk Evaluation 3.1 Radionuclides of Potential Ecological Concern The radionuclide evaluation follows the same basic procedures used for the chemical ecological risk  evaluation (Section 2.0 of this appendix). Information and analyses presented here is limited to those items  specific to radionuclides.   Radionuclides of potential ecological concern (RPECs) for this ERA were identified from existing soil data that  were evaluated and reduced according to the data reduction procedures presented in the SRAM Rev. 2  Addendum (MWH, 2014).   A summary of the soil samples analyzed for radionuclides and included in the ERA for the EEL RFI site is  presented in Table 11 in Attachment 1. Radionuclides detected in soils and summary statistics are presented  in Tables 12 and 13, respectively, in Attachment 1.   RPECs were identified as radionuclides detected in soil meeting the following criteria:   Radionuclide was detected at the site using validated laboratory analyses.    Radionuclide was present in excess of background (where background information is available). The  background evaluation consisted of the following:    If the maximum detection was below the BTV (95/95 UTL for soil), then that radionuclide was not a  RPEC.   If the maximum detection was above the background comparison value and sufficient data are  available, a more rigorous statistical evaluation was conducted to determine whether the  population of site data was statistically different than the background population.  Radionuclides for which the maximum detection exceeded two times the soil background comparison  value were retained as a RPEC, regardless of the outcome of the statistical background evaluation.   The selection of RPECs is shown in Table E2‐12.   3.2 Radionuclide Exposure Characterization 3.2.1.1 Exposure Scenarios  The exposure characterization is used to evaluate the relationship between ecological receptors at or near  the site and potential stressors (RPECs). Media and receptors of potential ecological concern were identified  as part of the EcoCSM (Section 2.1.2 of this appendix).    Exposure scenarios evaluated for radionuclides are dependent on the available screening levels and are  limited to a general ‘biota’ category for soils in the exposure depth interval of concern. Radionuclide data  were collected at the surface, so the exposure depth is 0 to 2 feet bgs.    3.2.1.2 Exposure Point Concentrations  EPCs are calculated in the same manner as for CPECs, discussed in Section 2.2.1 of this appendix. EPCs for  RPECs in soil (0 to 2 feet bgs) are summarized in Table E2‐13.   3.3 Radionuclide Ecological Effects Characterization Evaluation of radionuclides uses the methods and biota concentration guides (BCGs) for terrestrial biota as  presented in DOE Standard ‐ Graded Approach for Evaluating Radiation Doses to Aquatic and Terrestrial  Biota (United States Department of Energy, 2002). The Tier 1 Soil BCGs are concentration based values that  provide a conservative estimate of environmental compliance.   EN0411151012BAO 9 APPENDIX E2 ECOLOGICAL RISK ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE 3.4 Radionuclide Risk Characterization 4.0 Summary of Ecological Risk Assessment Risk estimates for radionuclides in soils were calculated by dividing the EPC by the Tier 1 BCG. Results are  presented in Table E2‐14. None of the RPECs exceeded available BCGs. No radionuclides of ecological  concern (ROECs) were identified.  This ERA for the EEL RFI site was conducted in accordance with risk assessment guidance provided in the  SRAM Rev. 2 Addendum (MWH, 2014). Potential risks from chemical and radionuclides were evaluated for  terrestrial receptors, including terrestrial plants, soil invertebrates, birds (hermit thrush), and mammals  (deer mouse). COECs/ROECs are those CPECs/RPECs identified during the ERA as primary contributors  posing unacceptable risk and are therefore retained for further evaluation during the CMS. For this ERA, the  following risk drivers were identified:     Soil COECs: dioxins and furans TEQ for mammals  Soil vapor COECs: none  Soil ROECs: none  Appendix E3 identifies CMS and NFA areas based on the HHRA and ERA results.  5.0 Uncertainty Analysis Uncertainties associated with the results of the ERA are a function of both the “state of the practice” of risk  assessment in general and uncertainty factors specific to an RFI site. The EEL RFI site ERA is subject to  uncertainty with regard to a variety of factors that include:       Environmental sampling and analysis  Fate and transport estimation  Exposure assessment  Toxicity assessment  Risk characterization  Uncertainties inherent in the current state of practice for ERAs and those specific to the EEL RFI site are  summarized in Table E2‐15.  6.0 References California Environmental Protection Agency, Department of Toxic Substances Control. 2012. Final Chemical  Soil Background Study Report. December 28.  CH2M HILL. 2008. Group 5 – Central Portions of Areas III and IV RCRA Facility Investigation Report, Santa  Susana Field Laboratory, Ventura County, California. November.  CH2M HILL. 2013a. Integration of the Surficial Media Operable Unit Risk Assessment Methodology and the  Data Quality Objectives Process, Boeing RCRA Facility Investigation, Santa Susana Field Laboratory, Ventura  County, California. March 8.  CH2M HILL. 2013b. Addendum to Master RCRA Facility Investigation Data Gap Work Plan, Boeing RFI  Subarea 5/9 South, EEL RFI Site, Santa Susana Field Laboratory, Ventura County, California. May.  MWH. 2014. Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field  Laboratory, Ventura County, California. August.  United States Department of Energy. 2002. DOE Standard ‐ Graded Approach for Evaluating Radiation Doses  to Aquatic and Terrestrial Biota. DOE‐STD‐1153‐2002. July.    10 EN0411151012BAO Tables List of Tables E2‐1  E2‐2  E2‐3  E2‐4  E2‐5  E2‐6  E2‐7  E2‐8  E2‐9  E2‐10  E2‐11  E2‐12  E2‐13  E2‐14  E2‐15  E2‐16    Summary of Habitats and Representative Species Evaluated  Selection of Chemicals of Potential Ecological Concern  Exposure Point Concentrations for CPECs in Soil  Exposure Point Concentrations for CPECs in Soil Vapor  Risk Estimation for Terrestrial Plants ‐ Exposure to Soil  Risk Estimation for Soil Invertebrates ‐ Exposure to Soil  Risk Estimation for Birds ‐ Food Chain Uptake via Soil  Risk Estimation for Mammals ‐ Food Chain Uptake via Soil  Incremental Risk Estimation for Soil Exposures  Risk Estimation for Mammals ‐ Inhalation of Soil Vapor  Weight‐of‐Evidence Evaluation  Selection of Radionuclides of Potential Ecological Concern  Exposure Point Concentrations for Radionuclides of Potential Ecological Concern in Soil  Risk Estimation for Terrestrial Biota ‐ Food Chain Uptake via Soil  Uncertainty Analysis  Risk Drivers for Corrective Measures Study    EN0411151012BAO TABLE E2‐1 Summary of Habitats and Representative Species Evaluated RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Habitat  Media Soil Terrestrial Soil Vapor Shallow Groundwater Sediment Aquatic/Wetland Surface Water EN0411151012BAO  Representative Species Terrestrial plants Soil invertebrates Hermit thrush Deer mouse Red‐tailed hawk Mule deer Bobcat Deer mouse Terrestrial plants Benthic macroinvertebrates Great blue heron Aquatic plants Aquatic invertebrates Fish Evaluated at This  Site Notes Yes Plant stress not observed, evaluated to be conservative. Yes Yes Yes No Large‐home‐range receptors will be evaluated in the Large‐Home‐ Range Receptor ERA. Yes No Groundwater does not occur from 0 to 6 feet bgs. No Ponded areas are not present at this site. No Ponded areas are not present at this site. PAGE 1 OF 1 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Measured Data Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO   Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft Type  ERAClass I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I O O O O O O O Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Preferred Analyte Name Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Phosphate Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin Units Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.024 33200 7.5 110 189 1.3 9.99 0.751 32.9 12.7 25.6 3.1 3.2 16.5 33.6 887 0.033 0.961 24.7 3.3 7.8 0.82 1 0.39 3.5 31.5 0.419 1320 58.9 126 5.74 0.099 0.046 0.000181 0.00149 0.0000157 0.00000703 0.0000191 0.000649 37900 0.497 24.2 203.8 1.424 18.85 0.435 60.11 26.18 42 5.387 1.129 33.9 64.4 723 0.028 1.642 64.2 11.73 11.73 ‐‐ 863.2 0.536 0.095 79.1 0.629 1865 111.8 153 10.64 ‐‐ ‐‐ 6.94E‐07 2.41E‐06 6.55E‐08 1.25E‐07 7.61E‐08 Yes No Yes Yes No No No Yes No No No No Yes No No Yes Yes No No No No ‐‐ No No Yes No No No No No No ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes No Yes Yes No No No No No No No No Yes No No No No No No No No ‐‐ No No Yes No No No No No No ‐‐ ‐‐ Yes Yes Yes Yes Yes Site > Bkgd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd ‐‐ ‐‐ ‐‐ nsd Site > Bkgd nsd nsd nsd nsd nsd nsd ‐‐ ‐‐ Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes No Yes Yes No No No No No No No No Yes No No No No No No No No Yes No No Yes No No No No No No Yes Yes Yes Yes Yes Yes Yes PAGE 1 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO   Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft Type  ERAClass O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Preferred Analyte Name 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Units Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.00000773 0.0000617 0.00000184 0.0000416 0.0000102 0.0000098 0.0000109 0.00000281 0.0000011 0.00000229 0.000025 0.0000519 0.0428 0.000642 0.032 0.94 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.0012 0.0015 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.0029 0.019 0.00073 0.00055 0.00055 1.69E‐07 7.39E‐07 9.84E‐07 9.95E‐07 1.64E‐07 1.00E‐07 1.81E‐07 2.18E‐07 2.76E‐08 2.81E‐07 8.06E‐07 5.63E‐07 1.67E‐05 1.19E‐06 0.027 0.398 0.001222 0.00164 0.003264 0.001177 0.00353 0.002457 0.00102 0.000792 0.002586 0.0018 0.0018 0.0018 0.000815 0.000645 0.002466 0.001805 0.0017 0.001864 0.000186 0.004164 0.006101 0.000126 0.0000826 0.000178 Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes Yes Yes No Yes Yes No Yes Yes Yes Yes Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd ‐‐ Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd nsd nsd nsd nsd nsd nsd High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes PAGE 2 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO   Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft Type  ERAClass O O O O O O O O O O O O I I I I I I I I I I I I I I I I I I I I I I I I I I I I Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC VOC VOC VOC Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Preferred Analyte Name Endrin Endrin aldehyde Heptachlor epoxide Mirex bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Methylene chloride Styrene Xylenes, Total Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Phosphate Selenium Silver Strontium Thallium Titanium Units mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb 0.0005 0.0011 0.00047 0.0047 0.0287 0.013 0.00597 0.0023 0.099 0.0027 0.000723 0.000372 0.024 33200 7.5 110 189 1.3 9.99 0.751 38.5 12.7 25.6 3.1 3.2 16.5 53.4 887 0.033 0.961 32.2 3.3 7.8 0.82 1 0.39 3.5 31.5 0.419 1320 0.000159 0.00037 0.00011 0.000279 0.028 0.043 0.0995 0.00837 0.00637 ‐‐ ‐‐ ‐‐ 0.000649 37900 0.497 24.2 203.8 1.424 18.85 0.435 60.11 26.18 42 5.387 1.129 33.9 64.4 723 0.028 1.642 64.2 11.73 11.73 ‐‐ 863.2 0.536 0.095 79.1 0.629 1865 Yes Yes Yes Yes Yes No No No Yes ‐‐ ‐‐ ‐‐ Yes No Yes Yes No No No Yes No No No No Yes No No Yes Yes No No No No ‐‐ No No Yes No No No Yes Yes Yes Yes No No No No Yes ‐‐ ‐‐ ‐‐ Yes No Yes Yes No No No No No No No No Yes No No No No No No No No ‐‐ No No Yes No No No nsd nsd nsd Site > Bkgd nsd nsd nsd nsd Site > Bkgd ‐‐ ‐‐ ‐‐ Site > Bkgd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd ‐‐ ‐‐ ‐‐ nsd Site > Bkgd nsd nsd nsd High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes No No No No Yes Yes Yes Yes Yes No Yes Yes No No No No No No No No Yes No No No No No No No No Yes No No Yes No No No PAGE 3 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO   Depth  Interval 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft Type  ERAClass I I I O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Preferred Analyte Name Vanadium Zinc Zirconium Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Units Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  73 126 8.19 0.099 0.046 0.00149 0.000181 0.0000157 0.0000191 0.00000703 0.0000617 0.00000773 0.0000416 0.00000184 0.0000098 0.0000102 0.0000109 0.00000281 0.0000011 0.00000229 0.000025 0.0000519 0.0428 0.000642 0.032 0.94 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.0012 0.0015 0.017 0.0021 0.13 111.8 153 10.64 ‐‐ ‐‐ 0.00000241 0.000000694 6.55E‐08 7.61E‐08 0.000000125 0.000000739 0.000000169 0.000000995 0.000000984 0.0000001 0.000000164 0.000000181 0.000000218 2.76E‐08 0.000000281 8.0603E‐07 0.000000563 0.0000167 0.000001193 0.027 0.398 0.001222 0.00164 0.003264 0.001177 0.00353 0.002457 0.00102 0.000792 0.002586 0.0018 0.0018 0.0018 0.000815 0.000645 No No No ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes No No No ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes nsd nsd nsd ‐‐ ‐‐ Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd ‐‐ Site > Bkgd Site > Bkgd High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes PAGE 4 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO   Depth  Interval 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft Type  ERAClass O O O O O O O O O O O O O O O O O O O O O O I I I I I I I I I I I I I I I I I I PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC VOC VOC VOC Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Preferred Analyte Name Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex beta‐BHC Butyl benzyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Diethyl phthalate bis(2‐Ethylhexyl) phthalate Methylene chloride Styrene Xylenes, Total Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Units mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb 2.3 0.015 0.0022 0.91 0.0018 0.0029 0.019 0.00055 0.00055 0.0005 0.0011 0.00047 0.0047 0.00073 0.013 0.0023 0.099 0.00597 0.0287 0.0027 0.000723 0.000372 0.043 33200 7.5 110 230 1.9 10.1 0.751 38.5 18.5 25.6 11.2 3.2 16.5 58 887 0.033 0.961 0.002466 0.001805 0.0017 0.001864 0.000186 0.004164 0.006101 0.0000826 0.000178 0.000159 0.00037 0.00011 0.000279 0.000126 0.043 0.00837 0.00637 0.0995 0.028 ‐‐ ‐‐ ‐‐ 0.000649 37900 0.497 24.2 203.8 1.424 18.85 0.435 60.11 26.18 42 5.387 1.129 33.9 64.4 723 0.028 1.642 Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes No No Yes No Yes ‐‐ ‐‐ ‐‐ Yes No Yes Yes Yes Yes No Yes No No No Yes Yes No No Yes Yes No Yes Yes No Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes No No Yes No No ‐‐ ‐‐ ‐‐ Yes No Yes Yes No No No No No No No Yes Yes No No No No No Site > Bkgd nsd Site > Bkgd Site > Bkgd nsd nsd nsd nsd nsd nsd nsd nsd Site > Bkgd nsd nsd nsd Site > Bkgd nsd nsd ‐‐ ‐‐ ‐‐ Site > Bkgd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes No No Yes No No Yes Yes Yes Yes No Yes Yes No No No No No No No Yes Yes No No No No No PAGE 5 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO   Depth  Interval 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft Type  ERAClass I I I I I I I I I I I I I I O O O O O O O O O O O O O O O O O O O O O O O O O O Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides Herbicides PAH‐HighMW Preferred Analyte Name Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Phosphate Selenium Silver Strontium Thallium Tin Titanium Vanadium Zinc Zirconium Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4‐Dichlorophenoxybutyric acid MCPA Silvex Benzo(a)anthracene Units Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  32.2 3.3 7.8 0.82 1 0.51 3.5 41.3 0.427 0.384 1320 73 126 8.19 0.099 0.046 0.00706 0.000181 0.00149 0.0000157 0.00000703 0.0000191 0.00000773 0.0000617 0.00000184 0.0000416 0.0000102 0.0000098 0.0000109 0.00000281 0.0000011 0.00000229 0.000025 0.0000519 0.000642 0.0428 0.032 0.94 0.0014 1.2 64.2 11.73 11.73 ‐‐ 863.2 0.536 0.095 79.1 0.629 3.83 1865 111.8 153 10.64 ‐‐ ‐‐ ‐‐ 6.94E‐07 2.41E‐06 6.55E‐08 1.25E‐07 7.61E‐08 1.69E‐07 7.39E‐07 9.84E‐07 9.95E‐07 1.64E‐07 1.00E‐07 1.81E‐07 2.18E‐07 2.76E‐08 2.81E‐07 8.06E‐07 5.63E‐07 1.19E‐06 1.67E‐05 0.027 0.398 0.000322 0.001222 No No No ‐‐ No No Yes No No No No No No No ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No No ‐‐ No No Yes No No No No No No No ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes nsd nsd ‐‐ ‐‐ ‐‐ nsd Site > Bkgd nsd nsd nsd nsd nsd nsd nsd ‐‐ ‐‐ ‐‐ Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd nsd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd nsd nsd Site > Bkgd High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No Yes No No Yes No No No No No No No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes PAGE 6 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Vapor Soil Vapor EN0411151012BAO   Depth  Interval 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft Type  ERAClass O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Acetone Ethylbenzene Methylene chloride Styrene Xylenes, Total 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Units mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  µg/L  µg/L Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.0012 0.012 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.0029 0.019 0.00073 0.00055 0.00055 0.0005 0.0011 0.00058 0.00047 0.0047 0.0503 0.013 0.00597 0.0023 0.099 0.016 0.000312 0.00281 0.000723 0.00136 1.5 1.5 0.00164 0.003264 0.001177 0.00353 0.002457 0.00102 0.000792 0.002586 0.0018 0.0018 0.0018 0.000815 0.000645 0.002466 0.001805 0.0017 0.001864 0.000186 0.004164 0.006101 0.000126 0.0000826 0.000178 0.000159 0.00037 0.000116 0.00011 0.000279 0.028 0.043 0.0995 0.00837 0.00637 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes Yes No No No Yes ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes No Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes No No No No Yes ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd Site > Bkgd ‐‐ Site > Bkgd Site > Bkgd Site > Bkgd nsd Site > Bkgd Site > Bkgd nsd nsd nsd nsd nsd nsd nsd nsd nsd nsd Site > Bkgd nsd nsd nsd nsd Site > Bkgd ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ High  SQLc CPEC ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes No No Yes Yes Yes Yes Yes Yes Yes Yes No Yes Yes Yes Yes Yes Yes Yes Yes Yes No No No No Yes Yes Yes Yes Yes Yes Yes Yes PAGE 7 OF 8 TABLE E2‐2 Selection of Chemicals of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix  Depth  Interval Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Soil Vapor 0‐6 ft Non‐Detect (SQL Screen)  Soil 0‐2 ft Soil 0‐2 ft Soil 0‐6 ft Type  ERAClass Preferred Analyte Name O O O O O O O O O VOC VOC VOC VOC VOC VOC VOC VOC VOC Benzene Chloroform Dichlorodifluoromethane Ethylbenzene Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Xylenes, Total O O O ARCL ARCL ARCL Aroclor‐1248 Aroclor‐1248 Aroclor‐1248 Units Maximum  Maximum  Maximum  Background  Exceeds  Exceeds 2x  Detect 95‐95UTL Background Backgrounda WRS‐Gehanb High  SQLc CPEC µg/L  µg/L µg/L  µg/L µg/L  µg/L µg/L  µg/L µg/L  0.13 0.0021 0.0014 0.12 0.0095 0.95 120 0.022 0.54 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Yes Yes Yes mg/kg mg/kg mg/kg ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes Yes Yes Yes Yes Notes: a  Analytes with a maximum detected concentration > 2x background were retained as CPECs regardless of the WRS results. b  Analytes where the site population was considered outside the background population as evaluated by WRS‐Gehan were retained as CPECs. c  Analytes that were never detected, but have a high percentage of SQLs>ESLs are selected as CPECs. ‐‐ = not applicable, not available µg/L = micrograms per liter BHC = benzene hexachloride CPEC = chemical of potential ecological concern ERA = ecological risk assessment ESL = ecological screening level  ft = feet  MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight NA = not available NSD = no significant difference PAH = polcyclic aromatic hydrocarbon RBSL = risk‐based screening level SQL = sample quantitation limit SVOC = semivolatile organic compound TEQ = toxicity equivalent  VOC = volatile organic compound WRS = Wilcoxon rank sum Yes = Analyte retained as a CPEC EN0411151012BAO  PAGE 8 OF 8 TABLE E2‐3 Exposure Point Concentrations for CPECs in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth  Maximum   Matrix Interval Type  EcoRAClass Chemical of Potential Ecological Concern Units Detect RME EPC RME EPC Basis Measured Data Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft EN0411151012BAO  I I I I I I O O O O O O O O O O O O O O O O O O O O O O O O O O O O Energetics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW Perchlorate Antimony Arsenic Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  2.4E‐02 7.5E+00 1.1E+02 3.2E+00 8.2E‐01 3.5E+00 9.9E‐02 4.6E‐02 1.8E‐04 1.5E‐03 1.6E‐05 7.0E‐06 1.9E‐05 7.7E‐06 6.2E‐05 4.2E‐05 1.0E‐05 9.8E‐06 1.1E‐05 2.8E‐06 1.1E‐06 2.3E‐06 2.5E‐05 5.2E‐05 4.3E‐02 6.4E‐04 3.2E‐02 9.4E‐01 1.2E+00 7.4E‐01 1.0E+00 2.3E‐01 5.2E‐01 1.5E+00 1.5E‐02 7.9E‐01 2.6E+01 1.1E+00 6.3E‐01 5.7E‐01 4.7E‐02 3.8E‐02 9.1E‐05 6.8E‐04 4.5E‐06 2.5E‐06 5.8E‐06 2.5E‐06 2.7E‐05 1.3E‐05 2.5E‐06 3.0E‐06 3.4E‐06 7.7E‐07 3.1E‐07 6.5E‐07 1.2E‐05 2.1E‐05 1.1E‐02 2.8E‐04 3.2E‐02 9.4E‐01 4.3E‐01 1.8E‐01 3.6E‐01 5.7E‐02 2.2E‐01 5.4E‐01 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Percentile Bootstrap) 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Adjusted Gamma UCL 95% Adjusted Gamma UCL 95% Adjusted Gamma UCL 95% KM (Chebyshev) UCL Maximum Result Maximum Result 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL PAGE 1 OF 5 TABLE E2‐3 Exposure Point Concentrations for CPECs in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth  Maximum   Matrix Interval Type  EcoRAClass Chemical of Potential Ecological Concern Units Detect RME EPC RME EPC Basis Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  O O O O O O O O O O O O O O O O O O O O O O O I I I I I I I O O O O O PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC VOC VOC VOC Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL ARCL Dioxin_Furans Dioxin_Furans Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex Di‐n‐octyl phthalate Methylene chloride Styrene Xylenes, Total Perchlorate Antimony Arsenic Fluoride Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  9.6E‐02 2.6E‐01 2.5E+00 1.7E‐02 2.1E‐03 1.3E‐01 2.3E+00 1.5E‐02 2.2E‐03 9.1E‐01 1.8E‐03 1.9E‐02 7.3E‐04 5.5E‐04 5.5E‐04 5.0E‐04 1.1E‐03 4.7E‐04 4.7E‐03 9.9E‐02 2.7E‐03 7.2E‐04 3.7E‐04 4.3E‐02 7.5E+00 1.1E+02 1.1E+01 3.2E+00 8.2E‐01 3.5E+00 9.9E‐02 4.6E‐02 7.1E‐03 1.8E‐04 1.5E‐03 1.1E‐02 6.8E‐02 9.1E‐01 1.1E‐02 2.0E‐03 5.1E‐02 8.3E‐01 6.8E‐03 1.6E‐03 2.2E‐01 1.8E‐03 6.4E‐03 7.3E‐04 5.5E‐04 5.5E‐04 5.0E‐04 1.1E‐03 4.7E‐04 1.8E‐03 1.8E‐02 2.7E‐03 5.5E‐04 3.7E‐04 1.2E‐02 5.5E‐01 1.6E+01 2.7E+00 9.3E‐01 6.1E‐01 2.5E‐01 3.3E‐02 1.1E‐02 7.1E‐03 6.0E‐05 8.4E‐04 95% KM (t) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (t) UCL 97.5% KM (Chebyshev) UCL Maximum Result 95% KM (BCA) UCL Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result 95% KM (t) UCL 95% KM (t) UCL Maximum Result 95% KM (t) UCL Maximum Result 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (Percentile Bootstrap) 95% KM (t) UCL Maximum Result 95% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL PAGE 2 OF 5 TABLE E2‐3 Exposure Point Concentrations for CPECs in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth  Maximum   Matrix Interval Type  EcoRAClass Chemical of Potential Ecological Concern Units Detect RME EPC RME EPC Basis Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4‐Dichlorophenoxybutyric acid MCPA Silvex Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/Kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  1.6E‐05 7.0E‐06 1.9E‐05 7.7E‐06 6.2E‐05 4.2E‐05 1.0E‐05 9.8E‐06 1.1E‐05 2.8E‐06 1.1E‐06 2.3E‐06 2.5E‐05 5.2E‐05 6.4E‐04 4.3E‐02 3.2E‐02 9.4E‐01 1.4E‐03 1.2E+00 7.4E‐01 1.0E+00 2.3E‐01 5.2E‐01 1.5E+00 9.6E‐02 2.6E‐01 2.5E+00 1.7E‐02 2.1E‐03 1.3E‐01 2.3E+00 1.5E‐02 2.2E‐03 9.1E‐01 2.9E‐06 1.7E‐06 3.8E‐06 1.6E‐06 1.8E‐05 8.7E‐06 1.6E‐06 2.0E‐06 2.2E‐06 4.8E‐07 2.0E‐07 4.2E‐07 8.6E‐06 1.6E‐05 1.9E‐04 9.2E‐03 2.6E‐02 9.4E‐01 1.4E‐03 1.2E‐01 7.6E‐02 1.4E‐01 2.5E‐02 5.9E‐02 2.1E‐01 6.6E‐03 2.9E‐02 2.5E‐01 6.8E‐03 2.0E‐03 1.4E‐02 2.3E‐01 3.5E‐03 1.5E‐03 5.4E‐02 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL Maximum Result Maximum Result 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL PAGE 3 OF 5 TABLE E2‐3 Exposure Point Concentrations for CPECs in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth  Maximum   Matrix Interval Type  EcoRAClass Chemical of Potential Ecological Concern Units Detect RME EPC RME EPC Basis Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Soil 0‐6 ft O Non‐Detect (SQL Screen)  Soil 0‐2 ft O Soil 0‐6 ft O Extrapolated Data Soil 0‐2 ft O Soil 0‐2 ft O Soil 0‐6 ft O Soil 0‐6 ft O Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC VOC VOC VOC VOC VOC 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex Di‐n‐octyl phthalate Acetone Ethylbenzene Methylene chloride Styrene Xylenes, Total mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  1.8E‐03 1.9E‐02 7.3E‐04 5.5E‐04 5.5E‐04 5.0E‐04 1.1E‐03 5.8E‐04 4.7E‐04 4.7E‐03 9.9E‐02 1.6E‐02 3.1E‐04 2.8E‐03 7.2E‐04 1.4E‐03 1.8E‐03 4.4E‐03 7.3E‐04 5.5E‐04 5.5E‐04 5.0E‐04 1.1E‐03 5.8E‐04 4.7E‐04 1.6E‐03 1.4E‐02 1.6E‐02 3.1E‐04 2.8E‐03 5.2E‐04 1.4E‐03 Maximum Result 95% KM (t) UCL Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result 95% KM (t) UCL 95% KM (t) UCL Maximum Result Maximum Result Maximum Result 95% KM (t) UCL Maximum Result ARCL ARCL Aroclor‐1248 Aroclor‐1248 mg/kg mg/kg #N/A #N/A 2.3E‐02 2.3E‐02 Mean Nondetect SQL Mean Nondetect SQL PCBs PCBs PCBs PCBs PCB_TEQ_Bird PCB_TEQ_Mammal PCB_TEQ_Bird PCB_TEQ_Mammal mg/kg mg/kg mg/kg mg/kg 2.5E‐04 1.1E‐04 2.5E‐04 1.1E‐04 1.4E‐04 6.2E‐05 7.6E‐05 3.3E‐05 Extrapolated Extrapolated Extrapolated Extrapolated Notes: *  ProUCL Version 5 does not offer a calculated UCL when there are too few unique detected results (one or sometimes more than one). In these      cases, the 95% Chebyshev UCL using a proxy value of 1/2 the detection limit for NDs was selected as the EPC.   PCB TEQs were extrapolated from Aroclor‐1254 and ‐1260 and represent dioxin‐like PCBs. BHC = benzene hexachloride CPEC = chemical of potential ecological concern EcoRBSL = ecological risk‐based screening level EPC = exposure point concentration ft bgs = feet below ground surface EN0411151012BAO  PAGE 4 OF 5 TABLE E2‐3 Exposure Point Concentrations for CPECs in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth  Maximum   Matrix Interval Type  EcoRAClass Chemical of Potential Ecological Concern Units Detect RME EPC RME EPC Basis KM = Kaplan Meier MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight PAH = polcyclic aromatic hydrocarbon PCB = polychlorinated biphenyl RME = reasonable maximum exposure  SVOC = semivolatile organic compound TEQ = toxicity equivalent  UCL = upper confidence limit on the mean VOC = volatile organic compound EN0411151012BAO  PAGE 5 OF 5 TABLE E2‐4 Exposure Point Concentrations for CPECs in Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California    Depth  EcoRAClas Chemical of Potential Ecological   Matrix Interval s Concern Units  RME EPC RME EPC Basis Measured Data Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Benzene Chloroform Dichlorodifluoromethane Ethylbenzene Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Xylenes, Total µg/L µg/L µg/L  µg/L µg/L µg/L  µg/L µg/L µg/L  µg/L µg/L  1.01 0.255 0.13 0.0021 0.0014 0.109 0.0095 0.203 15.3 0.022 0.133 99% KM (Chebyshev) UCL 95% KM (t) UCL Maximum Result Maximum Result Maximum Result 95% KM (t) UCL Maximum Result 95% KM (t) UCL 95% KM (t) UCL Maximum Result 95% KM (t) UCL Notes: *  ProUCL Version 5 does not offer a calculated UCL when there are too few unique detected results (one or sometimes more     than one). In these cases, the 95% Chebyshev UCL using a proxy value of 1/2 the detection limit for NDs was selected as      the EPC.   EPC = exposure point concentration KM = Kaplan Meier RME = reasonable maximum exposure  UCL = upper confidence limit on the mean VOC = volatile organic compound µg/L = micrograms per liter EN0411151012BAO  PAGE 1 OF 1 TABLE E2‐5 Risk Estimation for Terrestrial Plants ‐ Exposure to Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth   Matrix Interval  ERAClass Measured Data Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft EN0411151012BAO  Energetics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW Chemical of Potential Ecological Concern Perchlorate Antimony Arsenic Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Plant  Units RME EPC EcoRBSL mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.015 0.791 26.4 1.13 0.625 0.569 0.0473 0.0379 9.05E‐05 0.000677 4.53E‐06 2.49E‐06 5.77E‐06 2.52E‐06 2.71E‐05 0.000013 2.48E‐06 2.95E‐06 3.36E‐06 7.67E‐07 3.08E‐07 6.5E‐07 0.0112 0.00028 0.032 0.94 0.434 0.179 0.36 0.0568 0.219 0.538 0.0105 107 5 18 30 ‐‐ 560 40 40 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1.5 1.2 1.2 1.2 1.2 1.2 1.2 HQ Exceed RBSL? 1E‐04 2E‐01 1E+00 4E‐02 ‐‐ 1E‐03 1E‐03 9E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3E‐01 1E‐01 3E‐01 5E‐02 2E‐01 4E‐01 9E‐03 No No No No Uncertainty No No No Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty No No No No No No No PAGE 1 OF 3 TABLE E2‐5 Risk Estimation for Terrestrial Plants ‐ Exposure to Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth   Matrix Interval  ERAClass Soil 0‐2 ft PAH‐HighMW Soil 0‐2 ft PAH‐HighMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft SVOC Soil 0‐2 ft VOC Soil 0‐2 ft VOC Soil 0‐2 ft VOC Nondetect (SQL Screen) Data Soil 0‐2 ft ARCL Chemical of Potential Ecological Concern Plant  Units RME EPC EcoRBSL HQ Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex Di‐n‐octyl phthalate Methylene chloride Styrene Xylenes, Total mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.0675 0.905 0.0111 0.00197 0.0507 0.831 0.0068 0.00161 0.219 0.0018 0.00637 0.00073 0.00055 0.00055 0.0005 0.0011 0.00047 0.00184 0.0176 0.0027 0.000548 0.000372 1.2 1.2 20 20 2 1.9 1.2 100 1.2 12 12 1000 1000 1000 ‐‐ ‐‐ 1000 ‐‐ 200 ‐‐ 320 1000 6E‐02 8E‐01 6E‐04 1E‐04 3E‐02 4E‐01 6E‐03 2E‐05 2E‐01 2E‐04 5E‐04 7E‐07 6E‐07 6E‐07 ‐‐ ‐‐ 5E‐07 ‐‐ 9E‐05 ‐‐ 2E‐06 4E‐07 Exceed RBSL? No No No No No No No No No No No No No No Uncertainty Uncertainty No Uncertainty No Uncertainty No No Aroclor‐1248 mg/kg 0.0233 40 6E‐04 No Notes: ‐‐ = not applicable, not available BHC = benzene hexachloride ERA = ecological risk assessment EPC = exposure point concentration ft = feet  HQ = hazard quotient MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  EN0411151012BAO  PAGE 2 OF 3 TABLE E2‐5 Risk Estimation for Terrestrial Plants ‐ Exposure to Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth   Matrix Interval  ERAClass Chemical of Potential Ecological Concern Plant  Units RME EPC EcoRBSL HQ Exceed RBSL? MW = molecular weight PAH = polcyclic aromatic hydrocarbon RBSL = risk‐based screening level RME = reasonable maximum exposure  SQL = sample quantitation limit SVOC = semivolatile organic compound VOC = volatile organic compound bold = HQ>1 Yes = EPC exceeds the EcoRBSL EN0411151012BAO  PAGE 3 OF 3 TABLE E2‐6 Risk Estimation for Soil Invertebrates ‐ Exposure to Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California    Depth  Matrix Interval Measured Data Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft EN0411151012BAO   ERAClass Energetics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW Chemical of Potential Ecological Concern Perchlorate Antimony Arsenic Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene  Units RME EPC Invertebrate  EcoRBSL HQ Exceed RBSL? mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.015 0.791 26.4 1.13 0.625 0.569 0.0473 0.0379 0.0000905 0.000677 0.00000453 0.00000249 0.00000577 0.00000252 0.0000271 0.000013 0.00000248 0.00000295 0.00000336 7.67E‐07 3.08E‐07 0.00000065 0.00028 0.0112 0.032 0.94 0.434 0.179 0.36 0.0568 0.219 0.538 0.0105 ‐‐ 78 60 0.4 ‐‐ ‐‐ 500 500 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 ‐‐ ‐‐ 18 18 18 18 18 18 18 ‐‐ 1E‐02 4E‐01 3E+00 ‐‐ ‐‐ 9E‐05 8E‐05 2E‐04 1E‐03 9E‐06 5E‐06 1E‐05 5E‐06 5E‐05 3E‐05 5E‐06 6E‐06 7E‐06 2E‐06 6E‐07 1E‐06 6E‐04 2E‐02 ‐‐ ‐‐ 2E‐02 1E‐02 2E‐02 3E‐03 1E‐02 3E‐02 6E‐04 Uncertainty No No Yes Uncertainty Uncertainty No No No No No No No No No No No No No No No No No No Uncertainty Uncertainty No No No No No No No PAGE 1 OF 3 TABLE E2‐6 Risk Estimation for Soil Invertebrates ‐ Exposure to Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California    Depth  Matrix Interval  ERAClass Soil 0‐2 ft PAH‐HighMW Soil 0‐2 ft PAH‐HighMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft PAH‐LowMW Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft SVOC Soil 0‐2 ft VOC Soil 0‐2 ft VOC Soil 0‐2 ft VOC Nondetect (SQL Screen) Data 0‐2 ft ARCL Soil Chemical of Potential Ecological Concern Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex Di‐n‐octyl phthalate Methylene chloride Styrene Xylenes, Total  Units mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  RME EPC 0.0675 0.905 0.0111 0.00197 0.0507 0.831 0.0068 0.00161 0.219 0.0018 0.00637 0.00073 0.00055 0.00055 0.0005 0.0011 0.00047 0.00184 0.0176 0.0027 0.000548 0.000372 Invertebrate  EcoRBSL 18 18 29 29 29 29 29 29 29 12 12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 65 HQ 4E‐03 5E‐02 4E‐04 7E‐05 2E‐03 3E‐02 2E‐04 6E‐05 8E‐03 2E‐04 5E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 6E‐06 Exceed RBSL? No No No No No No No No No No No Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty Uncertainty No Aroclor‐1248 mg/kg 0.0233 500 5E‐05 No Notes: ‐‐ = not applicable, not available BHC = benzene hexachloride ERA = ecological risk assessment EPC = exposure point concentration ft = feet  HQ = hazard quotient MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  EN0411151012BAO  PAGE 2 OF 3 TABLE E2‐6 Risk Estimation for Soil Invertebrates ‐ Exposure to Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California    Depth  Matrix Interval  ERAClass Chemical of Potential Ecological Concern MW = molecular weight PAH = polcyclic aromatic hydrocarbon RBSL = risk‐based screening level RME = reasonable maximum exposure  SQL = sample quantitation limit  Units RME EPC Invertebrate  EcoRBSL HQ Exceed RBSL? SVOC = semivolatile organic compound VOC = volatile organic compound bold = HQ>1 Yes = EPC exceeds the EcoRBSL EN0411151012BAO  PAGE 3 OF 3 TABLE E2‐7 Risk Estimation for Birds ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data  Depth   Matrix Interval  ERAClass Measured Data Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft EN0411151012BAO  Energetics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Chemical of Potential Ecological  Concern Perchlorate Antimony Arsenic Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 DioxinFuran_TEQ_Bird 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Units mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  Risk Estimates ‐ Hermit Thrush Low  High  RME EPC EcoRBSL EcoRBSL 0.015 0.791 26.4 1.13 0.625 0.569 0.0473 0.0379 1.17E‐05 0.032 0.94 0.434 0.179 0.36 0.0568 0.219 0.538 0.0105 0.0675 0.905 0.0111 0.00197 0.0507 0.831 0.0068 0.00161 0.219 0.0018 0.00637 0.00073 0.00055 0.00055 0.0005 2.5 ‐‐ 36 ‐‐ ‐‐ 0.99 0.083 0.053 5.7E‐06 200 220 28 140 66 210 140 41 61 ‐‐ 36 1.1 0.33 2.2 54 0.89 26 1.3 0.0051 0.0035 0.73 13 13 0.0079 8 ‐‐ 150 ‐‐ ‐‐ 29 0.83 0.53 0.000057 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 11 3.3 22 ‐‐ 8.9 130 13 0.85 0.58 2.9 ‐‐ ‐‐ 0.079 Exceed Low or  AUF 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 HQ ‐ Low HQ ‐ High High EcoRBSL? 6E‐03 ‐‐ 7E‐01 ‐‐ ‐‐ 6E‐01 6E‐01 7E‐01 2E+00 2E‐04 4E‐03 2E‐02 1E‐03 5E‐03 3E‐04 2E‐03 1E‐02 2E‐04 ‐‐ 3E‐02 1E‐02 6E‐03 2E‐02 2E‐02 8E‐03 6E‐05 2E‐01 4E‐01 2E+00 1E‐03 4E‐05 4E‐05 6E‐02 2E‐03 ‐‐ 2E‐01 ‐‐ ‐‐ 2E‐02 6E‐02 7E‐02 2E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1E‐03 6E‐04 2E‐03 ‐‐ 8E‐04 1E‐05 2E‐02 2E‐03 1E‐02 3E‐04 ‐‐ ‐‐ 6E‐03 No Uncertainty No Uncertainty Uncertainty No No No Yes No No No No No No No No No Uncertainty No No No No No No No No No Yes No No No No PAGE 1 OF 3 TABLE E2‐7 Risk Estimation for Birds ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data  Depth   Matrix Interval  ERAClass Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft Pesticides Soil 0‐2 ft SVOC Soil 0‐2 ft VOC Soil 0‐2 ft VOC Soil 0‐2 ft VOC Nondetect (SQL Screen) Data 0‐2 ft ARCL Soil Extrapolated Data Soil 0‐2 ft PCBs Hazard Indices Chemical of Potential Ecological  Concern Risk Estimates ‐ Hermit Thrush Units Low  High  RME EPC EcoRBSL EcoRBSL Endrin aldehyde Heptachlor epoxide Mirex Di‐n‐octyl phthalate Methylene chloride Styrene Xylenes, Total mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.0011 0.00047 0.00184 0.0176 0.0027 0.000548 0.000372 0.0092 1.1 220 13 ‐‐ ‐‐ 1090 0.092 5.6 ‐‐ 130 ‐‐ ‐‐ ‐‐ 1 1 1 1 1 1 1 1E‐01 4E‐04 8E‐06 1E‐03 ‐‐ ‐‐ 3E‐07 1E‐02 8E‐05 ‐‐ 1E‐04 ‐‐ ‐‐ ‐‐ No No No No Uncertainty Uncertainty No Aroclor‐1248 mg/kg 0.0233 0.094 0.94 1 2E‐01 2E‐02 No PCB_TEQ_Bird mg/kg 0.000145 5.7E‐06 5.7E‐05 1 3E+01 3E+00 Yes 1E+00 2E+00 6E‐02 2E‐01 2E+00 1E‐01 2E‐01 ‐‐ 2E‐02 3E‐02 No Yes No No Yes Aroclor HI Dioxin_Furan TEQ PAH‐HighMW HI PAH‐LowMW HI OC Pesticide HI Exceed Low or  AUF HQ ‐ Low HQ ‐ High High EcoRBSL? Notes: Hazard indices computed using measured data only. (non‐detect and extrapolated values are not included)  ‐‐ = not applicable, not available BHC = benzene hexachloride ERA = ecological risk assessment EPC = exposure point concentration ft = feet  HI = hazard index HQ = hazard quotient MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight PAH = polcyclic aromatic hydrocarbon RBSL = risk‐based screening level RME = reasonable maximum exposure  SQL = sample quantitation limit EN0411151012BAO  PAGE 2 OF 3 TABLE E2‐7 Risk Estimation for Birds ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data  Depth   Matrix Interval  ERAClass Chemical of Potential Ecological  Concern Units Risk Estimates ‐ Hermit Thrush Low  High  RME EPC EcoRBSL EcoRBSL Exceed Low or  AUF HQ ‐ Low HQ ‐ High High EcoRBSL? SVOC = semivolatile organic compound VOC = volatile organic compound bold = HQ>1 Yes = EPC exceeds the EcoRBSL EN0411151012BAO  PAGE 3 OF 3 TABLE E2‐8 Risk Estimation for Mammals ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data Risk Estimates ‐Deer Mouse  Depth   Matrix Interval  ERAClass Chemical of Potential Ecological  Concern Units Low  High  RME EPC EcoRBSL EcoRBSL Measured Data Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Perchlorate Antimony Arsenic Fluoride Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 DioxinFuran_TEQ_Mammal 2,4‐Dichlorophenoxybutyric acid MCPA Silvex Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  0.0121 0.546 16.1 2.68 0.928 0.611 0.249 0.0329 0.0105 0.00706 1.57E‐05 0.0257 0.94 0.0014 0.122 0.0759 0.138 0.0249 0.0586 0.205 0.00655 0.0288 0.254 0.00681 0.00196 0.0143 0.234 0.00345 0.00148 0.054 0.0018 EN0411151012BAO  Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL ARCL Dioxin_Furans Herbicides Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides 0.5 0.042 2.1 140 7.3 ‐‐ 3.5 0.039 0.025 0.039 5E‐07 6.2 0.12 0.55 0.81 5.1 2.4 7.4 4.9 1.2 2.3 4.8 1.2 63 26 140 160 55 37 68 0.55 7.7 2 31 240 30 ‐‐ 69 0.39 0.25 0.39 0.000005 19 0.61 1.8 50 310 150 460 310 76 140 300 73 340 140 770 880 300 200 370 11 AUF HQ  Low HQ High Exceed Low  or High  EcoRBSL? 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2E‐02 1E+01 8E+00 2E‐02 1E‐01 ‐‐ 7E‐02 8E‐01 4E‐01 2E‐01 3E+01 4E‐03 8E+00 3E‐03 2E‐01 1E‐02 6E‐02 3E‐03 1E‐02 2E‐01 3E‐03 6E‐03 2E‐01 1E‐04 8E‐05 1E‐04 1E‐03 6E‐05 4E‐05 8E‐04 3E‐03 2E‐03 3E‐01 5E‐01 1E‐02 3E‐02 ‐‐ 4E‐03 8E‐02 4E‐02 2E‐02 3E+00 1E‐03 2E+00 8E‐04 2E‐03 2E‐04 9E‐04 5E‐05 2E‐04 3E‐03 5E‐05 1E‐04 3E‐03 2E‐05 1E‐05 2E‐05 3E‐04 1E‐05 7E‐06 1E‐04 2E‐04 No Yes Yes No No Uncertainty No No No No Yes No Yes No No No No No No No No No No No No No No No No No No PAGE 1 OF 3 TABLE E2‐8 Risk Estimation for Mammals ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data Risk Estimates ‐Deer Mouse AUF HQ  Low HQ High 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1E‐02 1E‐03 3E‐03 2E‐03 6E‐03 1E‐02 7E‐03 4E‐01 1E‐02 2E‐04 3E‐04 8E‐06 1E‐04 2E‐06 4E‐04 6E‐04 3E‐04 1E‐04 1E‐04 6E‐04 1E‐03 1E‐04 7E‐02 3E‐03 2E‐05 7E‐05 8E‐07 1E‐05 1E‐06 3E‐04 Exceed Low  or High  EcoRBSL? No No No No No No No No No No No No No No No 0.064 1 4E+00 4E‐01 Yes 5.0E‐06 1 7E+01 7E+00 Yes  Depth   Matrix Interval  ERAClass Chemical of Potential Ecological  Concern Units Low  High  RME EPC EcoRBSL EcoRBSL Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft Pesticides Soil 0‐6 ft SVOC Soil 0‐6 ft VOC Soil 0‐6 ft VOC Soil 0‐6 ft VOC Soil 0‐6 ft VOC Soil 0‐6 ft VOC Nondetect (SQL Screen) Data Soil 0‐6 ft ARCL Extrapolated Data Soil 0‐6 ft PCBs Hazard Indices 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex Di‐n‐octyl phthalate Acetone Ethylbenzene Methylene chloride Styrene Xylenes, Total mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  0.00436 0.00073 0.00055 0.00055 0.0005 0.0011 0.00058 0.00047 0.00155 0.0141 0.016 0.000312 0.00281 0.000521 0.00136 0.38 0.59 0.22 0.23 0.088 0.1 0.087 0.0013 0.12 94 46 41 27 210 3.4 7.6 2.9 4.2 4.4 0.88 1 4.5 0.0065 0.61 930 230 410 230 420 4.2 Aroclor‐1248 mg/kg 0.0233 0.0064 PCB_TEQ_Mammal mg/kg 3.27E‐05 5.0E‐07 EN0411151012BAO  PAGE 2 OF 3 TABLE E2‐8 Risk Estimation for Mammals ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data  Depth   Matrix Interval  ERAClass Chemical of Potential Ecological  Concern Units Risk Estimates ‐Deer Mouse Low  High  RME EPC EcoRBSL EcoRBSL Aroclor HI Dioxin_Furan TEQ PAH‐HighMW HI PAH‐LowMW HI OC Pesticide HI AUF HQ  Low HQ High 1E+00 3E+01 6E‐01 3E‐03 4E‐01 1E‐01 3E+00 1E‐02 5E‐04 8E‐02 Exceed Low  or High  EcoRBSL? No Yes No No No Notes: Hazard indices computed using measured data only. (non‐detect and extrapolated values are not included)  ‐‐ = not applicable, not available AUF = area use factor BHC = benzene hexachloride ERA = ecological risk assessment EPC = exposure point concentration ft = feet  HQ = hazard quotient MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight PAH = polcyclic aromatic hydrocarbon PCB = polychlorinated biphenyl RBSL = risk‐based screening level RME = reasonable maximum exposure  SQL = sample quantitation limit SVOC = semivolatile organic compound VOC = volatile organic compound bold = HQ>1 Yes = EPC exceeds the EcoRBSL EN0411151012BAO  PAGE 3 OF 3 TABLE E2‐9 Incremental Risk Estimatation for Soil Exposures RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Hermit Thrush Soil Invertebrates (0‐2 ft bgs) Terrestrial Plants Chemicals of Potential  Low  High  Low  High  Ecological Concern with  Plant Site  Plant Bkg  Plant  Invert Site  Invert Bkg  Invert  EcoRBSL  EcoRBSL  Low Bkg  High Bkg  Low INCR  High INCR  EcoRBSL  EcoRBSL   Matrix  ERAClass Receptor HQs>1 HQ HQ INCR HQ HQ HQ INCR HQ HQ HQ HQ HQ HQ HQ HQ HQ Measured Data Soil Inorganics Antimony Soil Inorganics Arsenic Soil Inorganics Hexavalent Chromium Soil Dioxin_Furans DioxinFuran_TEQ_Bird Soil Dioxin_Furans DioxinFuran_TEQ_Mammal Soil Herbicides MCPA Soil Pesticides 4,4'‐DDT Nondetect (SQL Screen) Data Soil ARCL Aroclor‐1248 Extrapolated Data Soil PCBs PCB_TEQ_Bird PCB_TEQ_Mammal Soil PCBs Deer Mouse (0‐6 ft bgs) Low Bkg  High Bkg  Low INCR  High INCR  HQ HQ HQ HQ 2E‐01 1E+00 4E‐02 ‐‐ ‐‐ ‐‐ 5E‐04 5E‐02 6E‐01 2E‐02 ‐‐ ‐‐ ‐‐ 2E‐04 <1 <1 <1 ‐‐ ‐‐ ‐‐ <1 1E‐02 4E‐01 3E+00 ‐‐ ‐‐ ‐‐ 5E‐04 3E‐03 2E‐01 1E+00 ‐‐ ‐‐ ‐‐ 2E‐04 <1 <1 <1 ‐‐ ‐‐ ‐‐ <1 ‐‐ 7E‐01 ‐‐ 2E+00 ‐‐ 4E‐03 2E+00 ‐‐ 2E‐01 ‐‐ 2E‐01 ‐‐ ‐‐ 1E‐02 ‐‐ 3E‐01 ‐‐ 8E‐02 ‐‐ 6E‐04 7E‐01 ‐‐ 7E‐02 ‐‐ 8E‐03 ‐‐ ‐‐ 4E‐03 ‐‐ <1 ‐‐ 2E+00 ‐‐ <1 <1 ‐‐ <1 ‐‐ <1 ‐‐ ‐‐ <1 1E+01 8E+00 1E‐01 ‐‐ 3E+01 8E+00 1E‐02 3E‐01 5E‐01 3E‐02 ‐‐ 3E+00 2E+00 6E‐04 6E+00 5E+00 8E‐02 ‐‐ 6E‐01 1E+00 7E‐03 1E‐01 3E‐01 2E‐02 ‐‐ 6E‐02 2E‐01 3E‐04 7E+00 3E+00 <1 ‐‐ 3E+01 7E+00 <1 <1 <1 <1 ‐‐ 3E+00 <1 <1 6E‐04 ‐‐ bkg 5E‐05 ‐‐ bkg 2E‐01 2E‐02 ‐‐ ‐‐ bkg bkg 4E+00 4E‐01 ‐‐ ‐‐ bkg bkg ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3E+01 ‐‐ 3E+00 ‐‐ 8E‐02 ‐‐ 8E‐03 ‐‐ 3E+01 ‐‐ 2.5E+00 ‐‐ ‐‐ 7E+01 ‐‐ 7E+00 ‐‐ 6E‐01 ‐‐ 6E‐02 ‐‐ 6E+01 ‐‐ 6E+00 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 2E+00 2E‐01 1E‐02 8E‐02 7E‐01 8E‐03 4E‐03 2E+00 <1 <1 <1 3E+01 1E‐02 3E+00 6E‐04 6E‐01 7E‐03 6E‐02 3E‐04 3E+01 <1 3E+00 <1 Hazard Indices Dioxin_Furan TEQ OC Pesticide HI Notes: ‐‐ = not applicable, not available bkg = background value was not available to calculate a background HQ ERA = ecological risk assessment ft = feet  HI = hazard index HQ = hazard quotient INCR = incremental risk MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  PCB = polychlorinated biphenyl RBSL = risk‐based screening level SQL = sample quantitation limit TEQ = toxicity equivalent bold = site or incremental HQ>1 EN0411151012BAO  PAGE 1 OF 1 TABLE E2‐10 Risk Estimation for Mammals ‐ Inhalation of Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Site Data  Matrix  Depth  Interval  ERAClass Measured Data Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Chemical of Potential Ecological  Concern 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Benzene Chloroform Dichlorodifluoromethane Ethylbenzene Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Xylenes, Total Units µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L µg/L Risk Estimates ‐ Deer Mouse Low  High  RME EPC EcoRBSL EcoRBSL HQ ‐ Low HQ ‐ High 1.01 0.255 0.13 0.0021 0.0014 0.109 0.0095 0.203 15.3 0.022 0.133 250 1210 0.76 1.6 1210 31 32 0.22 8.5 1210 10 760 58900 3.8 8.1 58900 160 160 0.56 43 58900 52 4E‐03 2E‐04 2E‐01 1E‐03 1E‐06 4E‐03 3E‐04 9E‐01 2E+00 2E‐05 1E‐02 1E‐03 4E‐06 3E‐02 3E‐04 2E‐08 7E‐04 6E‐05 4E‐01 4E‐01 4E‐07 3E‐03 Exceed RBSL? No No No No No No No No Yes No No Notes:  µg/L = micrograms per liter  ERA = ecological risk assessment HQ = hazard quotient RBSL = risk‐based screening level RME = reasonable maximum exposure  VOC = volatile organic compound bold = HQ>1 Yes = EPC exceeds the EcoRBSL EN0411151012BAO  PAGE 1 OF 1 TABLE E2‐11 Weight‐of‐Evidence Evaluation RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Terrestrial Plants  Matrix Type  ERAClass SOIL Chemicals of Potential  Ecological Concern with  Receptor HQs>1 Hermit Thrush (0‐2 ft bgs) Soil Invertebrates Plant Site  Plant  Invert Site  Invert  HQ INCR HQ HQ INCR HQ Low  EcoRBSL  HQ Deer Mouse (0‐6 ft bgs) Low  High  EcoRBSL  Low INCR  High INCR  EcoRBSL  HQ HQ HQ HQ Weight of Evidence INCR HQ  INCR HQ  Exceeds  Exceeds  High  High  Potential  Low  EcoRBSL  Low INCR  High INCR  EcoRBSL Hotspot EcoRBSL HQ HQ HQ COEC COEC Depth  Interval Notes Measured Data Soil I Inorganics Soil I Inorganics Soil I Inorganics Antimony Arsenic Hexavalent Chromium <1 <1 <1 <1 <1 <1 <1 <1 3E+00 <1 <1 <1 ‐‐ <1 ‐‐ ‐‐ <1 ‐‐ ‐‐ <1 ‐‐ ‐‐ <1 ‐‐ 1E+01 8E+00 <1 <1 <1 <1 7E+00 3E+00 <1 <1 <1 <1 Yes Yes No No No No No No No No No No ‐‐ ‐‐ ‐‐ Incremental HQ<1 at High EcoRBSL. Incremental HQ<1 at High EcoRBSL. Incremental HQ<1 at High EcoRBSL. Soil O Dioxin_Furans DioxinFuran_TEQ_Bird ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 <1 2E+00 <1 ‐‐ ‐‐ ‐‐ ‐‐ Yes No No No ‐‐ Soil O Dioxin_Furans DioxinFuran_TEQ_Mammal ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3E+01 3E+00 3E+01 3E+00 Yes Yes Yes Yes 0‐6 ft MCPA 4,4'‐DDT ‐‐ <1 ‐‐ <1 ‐‐ <1 ‐‐ <1 <1 2E+00 ‐‐ <1 <1 <1 ‐‐ <1 8E+00 <1 2E+00 <1 7E+00 <1 <1 <1 Yes Yes No No No No No No ‐‐ ‐‐ Incremental HQ >1 at the  High EcoRBSL for  mammals only. Samples contributing to risk  extend to 6ft bgs. lf h ( bl ) Incremental HQ<1 at High EcoRBSL. Aroclor 1248 <1 bkg <1 bkg <1 <1 bkg bkg 4E+00 <1 bkg bkg No WOE No No No WOE ‐‐ Chemical was never detected, but was  retained for evaluation because SQLs  exceeded the Low EcoRBSL (SQL Screen). No  exceedances of the High EcoRBSL. Extrapolated Data Soil O PCBs PCB_TEQ_Bird ‐‐ ‐‐ ‐‐ ‐‐ 3E+01 3E+00 3E+01 3E+00 ‐‐ ‐‐ ‐‐ ‐‐ Yes Yes No No WOE ‐‐ Soil PCB_TEQ_Mammal ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7E+01 7E+00 6E+01 6E+00 Yes Yes No No WOE ‐‐ Incremental HQ>1 , however, extrapolated  data are not used for risk management  decisions. Results DioxinFuran_TEQs used for CMS  recommendations. Incremental HQ>1 , however, extrapolated  data are not used for risk management  decisions. Results DioxinFuran_TEQs used for CMS  recommendations. Dioxin_Furan TEQ ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 <1 2E+00 <1 3E+01 3E+00 3E+01 3E+00 Yes Yes Yes Soil O Herbicides Soil O Pesticides Non‐Detect (SQL Screen) Data Soil O ARCL O PCBs Incremental HQ<1 at High EcoRBSL. Hazard Indices Soil O Dioxin_Furans Soil O Pesticides Yes 0‐6 ft Incremental HQ >1 at the  High EcoRBSL for  mammals only. Samples contributing to risk  extend to 6ft bgs. Potential hotspot. OC Pesticide HI ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 <1 <1 <1 <1 <1 <1 <1 No No No No ‐‐ Incremental risk HQ <1 at High EcoRBSL. Trichloroethene ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 4E‐01 bkg bkg Yes No ‐‐ No ‐‐ Site risk HQ <1 at High EcoRBSL. SOIL VAPOR Soil Vapor VOC Notes:  ‐‐ = not applicable, not available bkg = background value was not available to calculate a background HQ CPEC = chemical of potential ecological concern ft bgs = feet below ground surface HI = hazard index HQ = hazard quotient INCR = incremental risk PCB = polychlorinated biphenyl SQL = sample quantitation limit TEQ = toxicity equivalent WOE = weight of evidence EN0411151012BAO  PAGE 1 OF 2 TABLE E2‐11 Weight‐of‐Evidence Evaluation RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Terrestrial Plants  Matrix Type  ERAClass Chemicals of Potential  Ecological Concern with  Receptor HQs>1 Hermit Thrush (0‐2 ft bgs) Soil Invertebrates Plant Site  Plant  Invert Site  Invert  HQ INCR HQ HQ INCR HQ Low  EcoRBSL  HQ Low  High  EcoRBSL  Low INCR  High INCR  EcoRBSL  HQ HQ HQ HQ Deer Mouse (0‐6 ft bgs) Weight of Evidence INCR HQ  INCR HQ  Exceeds  Exceeds  High  High  Potential  Low  EcoRBSL  Low INCR  High INCR  EcoRBSL Hotspot EcoRBSL HQ HQ HQ COEC COEC Depth  Interval Notes bold = site or incremental HQ>1 shading = retained as a COEC EN0411151012BAO  PAGE 2 OF 2 TABLE E2‐12 Selection of Radionuclides of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix  Depth  Interval Type  ERAClass Preferred Analyte Name Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R Actinium‐228 Americium‐241 Americium‐243 Antimony‐125 Barium‐137m Bismuth‐212 Bismuth‐214 Cesium‐134 Cesium‐137 Curium‐243/244 Europium‐155 Lead‐212 Lead‐214 Plutonium‐239/240 Plutonium‐244 Potassium‐40 Radon‐220 Radon‐222 Strontium‐90 Tellurium‐125m Thallium‐208 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Units Maximum  Maximum  Exceeds 2x  Maximum  Background  Exceeds  Detect 95‐95UTL Background Backgrounda pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g 1.32 0.0135 0.0129 0.119 0.0267 1.1 0.99 0.0109 0.0446 0.0128 0.089 1.64 1.06 0.00783 0.0022 20.1 1.37 1 0.275 0.0276 0.545 1.25 0.0454 0.958 1.23 1.76 0.852 0.0564 0.837 0.275 2.1 0.0142 0.0134 0.254 0.146 1.67 1.53 0.023 0.157 0.0147 0.156 2.48 1.64 0.00936 0.0014 26 2.01 1.6 0.0512 0.0595 0.803 2.995 0.0333 1.64 2.359 2.339 1.545 0.101 1.52 ‐‐ No No No No No No No No No No No No No No Yes No No No Yes No No No Yes No No No No No No ‐‐ No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No ‐‐ RPECb No No No No No No No No No No No No No No Yes No No No Yes No No No Yes No No No No No No Yes Notes: a  Analytes with a maximum detected concentration > 2x background were retained as CPECs regardless of the WRS results. b  Analytes that were never detected, but have a high percentage of SQLs>ESLs are selected as CPECs. ‐‐ = not applicable, not available EN0411151012BAO  PAGE 1 OF 2 TABLE E2‐12 Selection of Radionuclides of Potential Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Background Evaluation  Matrix  Depth  Interval Type  ERAClass Preferred Analyte Name Units Maximum  Maximum  Exceeds 2x  Maximum  Background  Exceeds  Detect 95‐95UTL Background Backgrounda RPECb BTV = background threshold value CPEC = chemical of potential ecological concern ft = feet  pCi/g =  picocuries per gram RPEC = radionuclide of potential ecological concern UTL = upper threshold limit Yes = Analyte retained as a CPEC EN0411151012BAO  PAGE 2 OF 2 TABLE E2‐13 Exposure Point Concentrations for Radionuclides of Potential Ecological Concern in Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Radionuclide of     Depth  Potential Ecological  Maximum  Matrix Interval Type  EcoRAClass Concern Units Detect RME EPC Measured Values Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft R R R R Radiochemistry Radiochemistry Radiochemistry Radiochemistry Plutonium‐244 Strontium‐90 Thorium‐229 Yttrium‐90 pCi/g pCi/g pCi/g pCi/g 0.0022 0.275 0.0454 0.275 0.0022 0.275 0.0454 0.275 RME EPC Basis Maximum Result Maximum Result Maximum Result Maximum Result Notes: EPC = exposure point concentration RME = reasonable maximum exposure  EN0411151012BAO  PAGE 1 OF 1 TABLE E2‐14 Risk Estimation for Terrestrial Biota ‐ Food Chain Uptake via Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California  Depth   Matrix Interval Measured Data Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft Type  ERAClass R R R R Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radionuclide of Potential  Ecological Concern Plutonium‐244 Strontium‐90 Thorium‐229 Yttrium‐90 Units RME EPC Biota  EcoRBSL HQ Exceed RBSL? pCi/g pCi/g pCi/g pCi/g 0.0022 0.275 0.0454 0.275 ‐‐ 22.5 789 ‐‐ ‐‐ 1E‐02 6E‐05 ‐‐ Uncertainty No No Uncertainty Notes: ‐‐ = not applicable, not available EPC = exposure point concentration ERA = ecological risk assessment HQ = hazard quotient pCi/g =  picocuries per gram RBSL = risk‐based screening level RME = reasonable maximum exposure  bold = HQ>1 EN0411151012BAO  PAGE 1 OF 1 TABLE E2‐15 Uncertainty Analysis RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Assessment Element Problem Formulation Fate and Transport Magnitude of  Impact Direction of Impact It is assumed that chemical concentrations will not change over time,  and that concentrations are constant during the exposure duration.  Natural attenuation and/or other degradation processes may be  significant in some areas resulting in an overestimation of exposure.  Moderate Over‐estimation of  exposure/risk Data Collection/Analysis Variability in analyses, laboratories, representativeness of samples,  sampling errors, and homogeneity of the sample matrix can influence  quality and quantity of data used in the risk assessment. Data were  validated, but historical sampling programs may not have had the  same standards as more recent ones. Unknown Over‐ or under‐estimation of  exposure/risk Data Collection/Analysis Detection Limits. Historical data were noted to have overly high  detection limits, especially in regard to metals. Recent sampling was  designed to have detection limits meeting EcoRBSLs. However, as  data are combined into the EPCs, high detection limits may influence  the resulting mean and 95UCLs. Moderate Over‐estimation of  exposure/risk Representative Species Representative species were selected to reduce uncertainty;  however, differences among species including physiology,  reproductive biology, and/or foraging habits can result in different  exposures and sensitivities for different receptors.  Low Over‐ or under‐estimation of  exposure/risk CPEC Selection SQL Comparison. Chemicals that were never detected at the site  were included as CPECs if they met the criteria in the SQL screening  process:  a) Mean Nondetect SQL > Minimum Low EcoRBSL. b) More than one sample was analyzed for that analyte. c) At least one other chemical in the same chemical class was  detected. Dermal and inhalation (for surface‐dwelling animals) exposure  pathways were not quantified. Low Over‐estimation of  exposure/risk Low Under‐estimation of  exposure/risk Exposure Pathway Analysis EN0411151012BAO  Uncertainty PAGE 1 OF 3 TABLE E2‐15 Uncertainty Analysis RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Assessment Element Analysis Bioavailability Area Use Factors Uncertainty Bioavailability of CPECs was assumed to be 100 percent. This likely  overestimates risk to receptors at the site. Area use factors of less than 1 were applied to exposure estimates for  wide‐ranging receptors (red‐tailed hawk, bobcat, and mule deer) in  the "refined" assessment to account for the foraging range of the  receptor. Use of the site may be greater or less than that predicted by  the area use factor. Exposure Point Concentrations RME EPC. The RME EPC is the 95UCL, unless the 95UCL exceeds the  maximum detect in which case the maximum detect is used as the  RME EPC. Use of the maximum detect is considered to be a likely  overestimation of the representative exposure point concentration  because samples were collected in areas likely to have the highest  concentrations at the site.  Exposure Point Concentrations The extrapolation of soil Aroclor‐1254 and Aroclor‐1260  concentrations to individual dioxin‐like PCB congener concentrations  introduces some uncertainty into the EPC estimates for the PCB  congeners. EcoRBSLs EN0411151012BAO  Toxicity data were not available for all CPECs or media considered in  the Group 5 ERAs. CPECs for which toxicity data were unavailable  were not evaluated, or surrogate toxicity data were used. Risks may  be overestimated or underestimated. Magnitude of  Impact Low Low Direction of Impact Over‐estimation of  exposure/risk Over‐ or under‐estimation of  exposure/risk Moderate Over‐estimation of  exposure/risk Low Over‐ or under‐estimation of  exposure/risk Moderate Over‐ or under‐estimation of  exposure/risk PAGE 2 OF 3 TABLE E2‐15 Uncertainty Analysis RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Assessment Element Risk Characterization Risk Estimation Risk Estimation Uncertainty Magnitude of  Impact Direction of Impact Potential ecological risks were quantified using the HQ approach. The  magnitude of the HQ indicates potential for ecological risk, but is not  an exact estimation of risk. For example, the actual risk from a  chemical with an HQ of 70 could be less than that for a chemical with  an HQ of 20 because of uncertainties involved in estimating exposure,  selection of effects criteria (threshold risk values), or field conditions  affecting exposure. Moderate Over‐ or under‐estimation of  risks Data necessary to estimate potential risks from all pathways for all  chemicals in the food‐chain uptake model were not always available.  For these chemicals and/or areas, the food‐chain uptake model was  completed using the available data. Moderate Under‐estimation of  exposure/risk Notes: CPEC = chemical of potential ecological concern EPC = exposure point concentration ERA = ecological risk assessment HQ = hazard quotient PCB = polychlorinated biphenyl RBSL = risk‐based screening level RME = reasonable maximum exposure SQL = sample quantitation limit UCL = upper confidence limit on the mean EN0411151012BAO  PAGE 3 OF 3 TABLE E2‐16 Risk Drivers for Corrective Measures Study RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Depth  Interval Notes Soil ‐ Measured Data Soil Dioxin_Furans DioxinFuran_TEQ_Mammal 0‐6 ft Incremental HQ >1 at the  High EcoRBSL for mammals only. Samples  contributing to risk extend to 6 ft bgs. Potential for hot spots Notes: bgs = below ground surface ft = feet HQ = hazard quotient RBSL = risk‐based screening level TEQ = toxicity equivalent EN0411151012BAO  PAGE 1 OF 1 Figure Ecological Receptors SPILLS ACCIDENTAL SPILLS AND RELEASES SOIL DUST and/or VOLATILE EMISSIONS BIOACCUMULATION TERRESTRIAL BIOTA Ingestion BIOACCUMULATION AQUATIC BIOTA Ingestion Root Contact Dermal Contact Ingestion SOIL ABOVEGROUND TANKS UNDERGROUND TANKS LEAKAGE SEDIMENT ROCKET TEST/DRAINAGE CHANNELS AND IMPOUNDMENTS LEACHING INFILTRATION PERCOLATION GROUNDWATER PRIOR WASTE DISPOSAL PRACTICES WATER EROSION RESUSPENSION SURFACE FLOW Terrestrial Plants Soil Invertebrates Great Blue Heron P P C P P P P P P C C C C C C P P C P P C P P C P C Root Contact C - Pathway considered complete for purposes of ecological risk assessment P - Pathway considered potentially complete Q - Pathway evaluated qualitatively unless site conditions indicate need for quantitative evaluation Pathways evaluated qualitatively or quantitatively in ecological risk assessment Root Contact Dermal Contact Ingestion pore water exchange SEDIMENT EEL_App_E2_ERA_tables_060815.xlsx, Figure E2-1_EcoCSM P P surface discharges SURFACE WATER WASTE DISPOSAL AREAS Inhalation (vapor) Inhalation (dust) Foliar Uptake Bobcat VOLATILIZATION AEOLIAN EROSION STORAGE EXPOSURE ROUTE Mule Deer TERTIARY SOURCE Deer Mouse SECONDARY RELEASE MECHANISM Red-tailed Hawk SECONDARY SOURCE TERRESTRIAL Hermit Thrush PRIMARY RELEASE MECHANISM Fish/Other Aquatic Organisms Aquatic Plants PRIMARY SOURCE Benthic Macroinvertebrates AQUATIC Root Contact Dermal Contact Ingestion Figure E2-1 Ecological Conceptual Site Model RCRA Facility Investigation, Data Summary and Findings R EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susa Ventura County, California 1 of 1 Attachment 1 Attachment 1 Tables 1  2  3  4  5  6  7  8  9  10  11  12  13  2 Analytes and CAS Numbers  Summary of Samples Used in the Ecological Risk Assessment  Detected Analytes in Media of Ecological Concern  Summary Statistics for Detected Analytes  Central Tendency Background Comparisons for Soil  Evaluation of SQLs for Chemicals Never Detected  Extrapolation of Aroclors to PCB Congeners in Soil – RME  Identification of Soil Depth Interval for Small Mammals  Summary of Hazard Quotients and Hazard Indices  Hot‐spot Evaluation for Soil  Summary of Samples Used in the Radionuclide Ecological Risk Assessment  Detected Analytes in Media of Ecological Concern  Summary Statistics for Detected Radionuclides  EN0411151012BAO ATTACHMENT 1, TABLE 1 Analytes and CAS Numbers RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Type I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I IG IG IG IG IG O O O O O O O O O EN0411151012BAO  CASNumber 14265442 14797730 16984488 18540299 57125 7429905 7439896 7439921 7439932 7439965 7439976 7439987 7440020 7440224 7440246 7440280 7440315 7440326 7440360 7440382 7440393 7440417 7440428 7440439 7440473 7440484 7440508 7440622 7440666 7440677 7782492 NO2 NO3 NO3N 14808798 16887006 24959679 7723140 E‐10139 630206 71556 79345 76131 79005 75343 75354 563586 67562394 PreferredAnalyte Phosphate Perchlorate Fluoride Hexavalent Chromium Cyanides Aluminum Iron Lead Lithium Manganese Mercury Molybdenum Nickel Silver Strontium Thallium Tin Titanium Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Vanadium Zinc Zirconium Selenium Nitrite‐NO2 Nitrate‐NO3 Nitrate‐N Sulfate Chloride Bromide Phosphorus pH 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3,4,6,7,8‐Heptachlorodibenzofuran PAGE 1 OF 6 ATTACHMENT 1, TABLE 1 Analytes and CAS Numbers RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O EN0411151012BAO  CASNumber 35822469 55673897 70648269 39227286 57117449 57653857 72918219 19408743 57117416 40321764 87616 96184 120821 95636 96128 106934 95501 107062 78875 122667 108678 541731 142289 99650 106467 90120 60851345 57117314 1746016 51207319 93765 95954 88062 118967 6629294 120832 94757 94826 105679 51285 121142 59229753 606202 35572782 75887 110758 91587 95578 PreferredAnalyte 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trichlorobenzene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,2‐Diphenylhydrazine 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,3‐Dinitrobenzene 1,4‐Dichlorobenzene 1‐Methyl naphthalene 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran 2,4,5‐T 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4,6‐Trinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,4‐Dichlorophenol 2,4‐Dichlorophenoxyacetic Acid (2,4‐D) 2,4‐Dichlorophenoxybutyric acid 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2,4‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2,6‐Dinitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Chloronaphthalene 2‐Chlorophenol PAGE 2 OF 6 ATTACHMENT 1, TABLE 1 Analytes and CAS Numbers RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O EN0411151012BAO  CASNumber 591786 91576 88744 88755 88722 91941 108689 99092 99081 72548 72559 50293 534521 19406510 101553 7005723 123422 100027 99990 83329 208968 67641 309002 319846 62533 120127 12674112 11104282 11141165 53469219 12672296 11097691 11096825 37324235 11100144 63496311 12642238 11126424 71432 92875 56553 50328 205992 191242 207089 65850 100516 319857 PreferredAnalyte 2‐Hexanone 2‐Methylnaphthalene 2‐Nitroaniline 2‐Nitrophenol 2‐Nitrotoluene 3,3'‐Dichlorobenzidine 3,5‐Dimethylphenol 3‐Nitroaniline 3‐Nitrotoluene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT 4,6‐Dinitro‐o‐cresol 4‐Amino‐2,6‐Dinitrotoluene 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Hydroxy‐4‐Methyl‐2‐pentanone 4‐Nitrophenol 4‐Nitrotoluene Acenaphthene Acenaphthylene Acetone Aldrin alpha‐BHC Aniline Anthracene Aroclor‐1016 Aroclor‐1221 Aroclor‐1232 Aroclor‐1242 Aroclor‐1248 Aroclor‐1254 Aroclor‐1260 Aroclor‐1262 Aroclor‐1268 Aroclor‐5432 Aroclor‐5442 Aroclor‐5460 Benzene Benzidine Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Benzoic acid Benzyl alcohol beta‐BHC PAGE 3 OF 6 ATTACHMENT 1, TABLE 1 Analytes and CAS Numbers RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O EN0411151012BAO  CASNumber 111911 111444 108601 117817 108861 74975 75274 75252 74839 85687 86748 56235 57749 108907 75003 67663 74873 79389 218019 156592 10061015 98828 75990 319868 53703 132649 124481 74953 1918009 75718 120365 60571 84662 108203 131113 84742 117840 88857 1746016‐TEQ_Bird 1746016‐TEQ_Mammal 122394 959988 33213659 1031078 72208 7421934 53494705 64175 PreferredAnalyte bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether bis(2‐Ethylhexyl) phthalate Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Butyl benzyl phthalate Carbazole Carbon Tetrachloride Chlordane Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene Chrysene cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Cumene Dalapon delta‐BHC Dibenzo(a,h)anthracene Dibenzofuran Dibromochloromethane Dibromomethane Dicamba Dichlorodifluoromethane Dichlorprop Dieldrin Diethyl phthalate Diisopropyl ether Dimethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Dinoseb DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Diphenylamine Endosulfan I Endosulfan II Endosulfan sulfate Endrin Endrin aldehyde Endrin ketone Ethanol PAGE 4 OF 6 ATTACHMENT 1, TABLE 1 Analytes and CAS Numbers RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O EN0411151012BAO  CASNumber 100414 206440 86737 50000 58899 76448 1024573 118741 87683 77474 67721 2691410 193395 78591 67630 94746 93652 67561 72435 78933 108101 1634044 75092 2385855 91203 104518 98953 55630 62759 621647 86306 103651 95498 95487 39001020 3268879 106478 59507 106434 106445 99876 36088229 87865 78115 85018 108952 100016 129000 PreferredAnalyte Ethylbenzene Fluoranthene Fluorene Formaldehyde gamma‐BHC Heptachlor Heptachlor epoxide Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane HMX Indeno(1,2,3‐cd)pyrene Isophorone Isopropanol MCPA MCPP Methanol Methoxychlor Methyl ethyl ketone Methyl isobutyl ketone (MIBK) Methyl tert‐butyl ether Methylene chloride Mirex Naphthalene n‐Butylbenzene Nitrobenzene Nitroglycerin n‐Nitrosodimethylamine n‐Nitrosodi‐n‐propylamine n‐Nitrosodiphenylamine n‐Propylbenzene o‐Chlorotoluene o‐Cresol Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin p‐Chloroaniline p‐Chloro‐m‐cresol p‐Chlorotoluene p‐Cresol p‐Cymene Pentachlorodibenzo‐p‐dioxins Pentachlorophenol PETN Phenanthrene Phenol p‐Nitroaniline Pyrene PAGE 5 OF 6 ATTACHMENT 1, TABLE 1 Analytes and CAS Numbers RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Type O O O O O O O O O O O O O O O O O O O O EN0411151012BAO  CASNumber 121824 135988 594207 93721 100425 99354 994058 75650 637923 98066 127184 479458 108883 8001352 156605 10061026 79016 75694 75014 1330207 PreferredAnalyte RDX sec‐Butylbenzene sec‐Dichloropropane Silvex Styrene sym‐Trinitrobenzene tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene Tetrachloroethene Tetryl Toluene Toxaphene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Trichloroethene Trichlorofluoromethane Vinyl chloride Xylenes, Total PAGE 6 OF 6 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID Soil D‐3‐03 ELBS01 ELBS02 ELBS02 ELBS02 ELBS02 ELBS02 ELBS03 ELBS04 ELBS05 ELBS05 ELBS06 ELBS07 ELBS10 ELBS1003 ELBS1004 ELBS1004 ELBS1005 ELBS1006 ELBS1007 ELBS1011 ELBS1011 ELBS1012 ELBS1013 ELBS1013 ELBS1014 ELBS1014 ELBS1014 ELBS1015 ELBS1015 ELBS1015 ELBS1016 ELBS1016 EN0411151012BAO  Sample ID D‐3‐03 RF246 RD247 RD248 RF247 RF248 RS691 RD976 RS504 RS505 RS647 RS645 RS646 RS887 ELBS1003S010 ELBS1004D010 ELBS1004S010 ELBS1005S010 ELBS1006S010 ELBS1007S010 ELBS1011S010 ELBS1011S060 ELBS1012S010 ELBS1013S010 ELBS1013S060 ELBS1014D010 ELBS1014S010 ELBS1014S050 ELBS1015S010 ELBS1015S060 ELBS1015X060 ELBS1016S010 ELBS1016S060 Sample Date Sample  Type Start  Depth  (ft) End  Depth  (ft) Plants Inverteb rates Birds 17‐Feb‐93 11‐Nov‐97 11‐Nov‐97 11‐Nov‐97 11‐Nov‐97 11‐Nov‐97 29‐Jan‐98 02‐Dec‐97 05‐Dec‐97 05‐Dec‐97 23‐Jan‐98 23‐Jan‐98 23‐Jan‐98 22‐Sep‐99 08‐Apr‐08 08‐Apr‐08 08‐Apr‐08 10‐Apr‐08 10‐Apr‐08 08‐Apr‐08 26‐Mar‐08 26‐Mar‐08 26‐Mar‐08 11‐Apr‐08 11‐Apr‐08 24‐Mar‐08 24‐Mar‐08 24‐Mar‐08 08‐Apr‐08 08‐Apr‐08 08‐Apr‐08 24‐Mar‐08 24‐Mar‐08 N N N N N N N N N N N N N N N FD N N N N N N N N N FD N N N N SS N N 0 0.5 0.5 6 0.5 6 0.5 0.5 0.5 0.5 4 0.5 0.5 0.5 0 0 0 0 0 0 0 5 0 0 5 0 0 4 0 5 5 0 5 0.5 0.5 0.5 6 0.5 6 0.5 0.5 0.5 0.5 4 0.5 0.5 0.5 1 1 1 1 1 1 1 6 1 1 6 1 1 5 1 6 6 1 6 x x x ‐‐ x ‐‐ x x x x ‐‐ x x x x x x x x x x ‐‐ x x ‐‐ x x ‐‐ x ‐‐ ‐‐ x ‐‐ x x x ‐‐ x ‐‐ x x x x ‐‐ x x x x x x x x x x ‐‐ x x ‐‐ x x ‐‐ x ‐‐ ‐‐ x ‐‐ x x x ‐‐ x ‐‐ x x x x ‐‐ x x x x x x x x x x ‐‐ x x ‐‐ x x ‐‐ x ‐‐ ‐‐ x ‐‐ Burrowing  Mammals Mammals x x x ‐‐ x ‐‐ x x x x ‐‐ x x x x x x x x x x ‐‐ x x ‐‐ x x ‐‐ x ‐‐ ‐‐ x ‐‐ x x x x x x x x x x x x x x x x x x x x x x x x x x x x x x x x x PAGE 1 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID ELBS1017 ELBS1017 ELBS1018 ELBS1018 ELBS1018 ELBS1018 ELBS1019 ELBS1019 ELBS1020 ELBS1021 ELBS1024 ELBS1024 ELBS1026 ELBS1026 ELBS1027 ELBS1027 ELBS1028 ELBS1028 ELBS1028 ELBS1028 ELBS1029 ELBS1029 ELBS13 ELBS14 ELBS1400 ELBS1401 ELBS1402 ELBS1402 ELBS1403 ELBS1403 ELBS1403 ELBS1405 ELBS1409 ELBS1410 EN0411151012BAO  Sample ID ELBS1017S010 ELBS1017S060 ELBS1018D010 ELBS1018S010 ELBS1018S060 ELBS1018X060 ELBS1019S010 ELBS1019S060 ELBS1020S010 ELBS1021S010 ELBS1024S010 ELBS1024S060 ELBS1026S010 ELBS1026S060 ELBS1027S010 ELBS1027S060 ELBS1028D010 ELBS1028S010 ELBS1028S060 ELBS1028X010 ELBS1029S010 ELBS1029X010 MT825 MT826 ELBS1400D01 ELBS1401S01 ELBS1402S01 ELBS1402X01 ELBS1403D01 ELBS1403S01 ELBS1403S02 ELBS1405S01 ELBS1409S01 ELBS1410S01 Sample Date 24‐Mar‐08 24‐Mar‐08 26‐Mar‐08 26‐Mar‐08 26‐Mar‐08 26‐Mar‐08 27‐Mar‐08 27‐Mar‐08 01‐Apr‐08 26‐Mar‐08 27‐Mar‐08 27‐Mar‐08 27‐Mar‐08 27‐Mar‐08 26‐Mar‐08 26‐Mar‐08 27‐Mar‐08 27‐Mar‐08 27‐Mar‐08 27‐Mar‐08 24‐Mar‐08 24‐Mar‐08 17‐Sep‐03 17‐Sep‐03 23‐May‐08 23‐May‐08 30‐May‐08 30‐May‐08 23‐May‐08 23‐May‐08 23‐May‐08 02‐Jun‐08 23‐May‐08 27‐May‐08 Sample  Type N N FD N N SS N N N N N N N N N N FD N N SS N SS N N FD N N SS FD N N N N N Start  Depth  (ft) 0 4.75 0 0 5 5 0 5 0 0 0 5 0 5 0 5 0 0 5 0 0 0 0 0 0 0 0.5 0.5 0 0 3 0.5 4 5 End  Depth  (ft) 1 5.75 1 1 6 6 1 6 1 1 1 6 1 6 1 6 1 1 6 1 1 1 0.5 0.5 1 1 1 1 1 1 4 1 5 6 Plants x ‐‐ x x ‐‐ ‐‐ x ‐‐ x x x ‐‐ x ‐‐ x ‐‐ x x ‐‐ x x x x x x x x x x x ‐‐ x ‐‐ ‐‐ Inverteb rates x ‐‐ x x ‐‐ ‐‐ x ‐‐ x x x ‐‐ x ‐‐ x ‐‐ x x ‐‐ x x x x x x x x x x x ‐‐ x ‐‐ ‐‐ Birds x ‐‐ x x ‐‐ ‐‐ x ‐‐ x x x ‐‐ x ‐‐ x ‐‐ x x ‐‐ x x x x x x x x x x x ‐‐ x ‐‐ ‐‐ Burrowing  Mammals Mammals x x ‐‐ x x x x x ‐‐ x ‐‐ x x x ‐‐ x x x x x x x ‐‐ x x x ‐‐ x x x ‐‐ x x x x x ‐‐ x x x x x x x x x x x x x x x x x x x x x x x ‐‐ x x x ‐‐ x ‐‐ x PAGE 2 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2000 ELBS2001 ELBS2001 ELBS2001 ELBS2002 ELBS2002 ELBS2002 ELBS2003 ELBS2003 ELBS2003 ELBS2004 ELBS2004 ELBS2004 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2005 ELBS2006 ELBS2006 ELBS2006 ELBS2006 ELBS2007 ELBS2007 ELBS2007 ELBS2007 ELBS2008 ELBS2008 ELBS2008 EN0411151012BAO  Sample ID ELBS2000D001 ELBS2000S001 ELBS2000S002 ELBS2000S003 ELBS2000S003SP ELBS2000S004 ELBS2001S001 ELBS2001S002 ELBS2001S003 ELBS2002S001 ELBS2002S002 ELBS2002S003 ELBS2003S001 ELBS2003S002 ELBS2003S003 ELBS2004S001 ELBS2004S002 ELBS2004S003 ELBS2005D003 ELBS2005S001 ELBS2005S002 ELBS2005S002SP ELBS2005S003 ELBS2006S001 ELBS2006S002 ELBS2006S003 ELBS2006S004 ELBS2007S001 ELBS2007S001SP ELBS2007S002 ELBS2007S003 ELBS2008D002 ELBS2008S001 ELBS2008S002 Sample Date 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 12‐Jun‐13 12‐Jun‐13 12‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 13‐Jun‐13 13‐Jun‐13 13‐Jun‐13 13‐Jun‐13 19‐Jun‐13 19‐Jun‐13 19‐Jun‐13 19‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 Sample  Type FD N N N SS N N N N N N N N N N N N N FD N N SS N N N N N N SS N N FD N N Start  Depth  (ft) 0 0 0.5 5 5 9 0 0.5 5 0 0.5 5 0 0.5 3.5 0 0.5 5 5 0 0.5 0.5 5 0 0.5 5 9 0 0 0.5 4 0.5 0 0.5 End  Depth  (ft) 0.5 0.5 1.5 6 6 10 0.5 1.5 6 0.5 1.5 6 0.5 1.5 4 0.5 1.5 6 6 0.5 1.5 1.5 6 0.5 1.5 6 10 0.5 0.5 1.5 5 1.5 0.5 1.5 Plants x x x ‐‐ ‐‐ ‐‐ x x ‐‐ x x ‐‐ x x ‐‐ x x ‐‐ ‐‐ x x x ‐‐ x x ‐‐ ‐‐ x x x ‐‐ x x x Inverteb rates x x x ‐‐ ‐‐ ‐‐ x x ‐‐ x x ‐‐ x x ‐‐ x x ‐‐ ‐‐ x x x ‐‐ x x ‐‐ ‐‐ x x x ‐‐ x x x Birds x x x ‐‐ ‐‐ ‐‐ x x ‐‐ x x ‐‐ x x ‐‐ x x ‐‐ ‐‐ x x x ‐‐ x x ‐‐ ‐‐ x x x ‐‐ x x x Burrowing  Mammals Mammals x x x x x x ‐‐ x ‐‐ x ‐‐ ‐‐ x x x x ‐‐ x x x x x ‐‐ x x x x x ‐‐ x x x x x ‐‐ x ‐‐ x x x x x x x ‐‐ x x x x x ‐‐ x ‐‐ ‐‐ x x x x x x ‐‐ x x x x x x x PAGE 3 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID ELBS2008 ELBS2009 ELBS2009 ELBS2009 ELBS2009 ELBS2010 ELBS2010 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2012 ELBS2015 ELBS2015 ELBS2016 ELBS2017 ELBS2018 ELBS2020 ELBS2020 ELBS2020 ELBS2021 ELBS2021 ELBS2021 ELBS2022 ELBS2022 ELBS2022 ELBS2022 ELBS2023 ELBS2023 ELBS2024 ELBS2024 ELBS2024 ELBS2025 ELBS2025 EN0411151012BAO  Sample ID ELBS2008S003 ELBS2009D003 ELBS2009S001 ELBS2009S002 ELBS2009S003 ELBS2010S001 ELBS2010S002 ELBS2012S001 ELBS2012S002 ELBS2012S003 ELBS2012S003SP ELBS2012S004 ELBS2015S001 ELBS2015S002 ELBS2016S001 ELBS2017S001 ELBS2018S001 ELBS2020S001 ELBS2020S002 ELBS2020S003 ELBS2021S001 ELBS2021S002 ELBS2021S003 ELBS2022D001 ELBS2022S001 ELBS2022S002 ELBS2022S003 ELBS2023S001 ELBS2023S002 ELBS2024S001 ELBS2024S002 ELBS2024S003 ELBS2025S001 ELBS2025S002 Sample Date 18‐Jun‐13 12‐Jun‐13 12‐Jun‐13 12‐Jun‐13 12‐Jun‐13 20‐Jun‐13 20‐Jun‐13 20‐Jun‐13 20‐Jun‐13 20‐Jun‐13 20‐Jun‐13 20‐Jun‐13 17‐Jun‐13 17‐Jun‐13 14‐Jun‐13 19‐Jun‐13 13‐Jun‐13 17‐Jun‐13 17‐Jun‐13 17‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 18‐Jun‐13 20‐Jun‐13 20‐Jun‐13 14‐Jun‐13 14‐Jun‐13 14‐Jun‐13 14‐Jun‐13 14‐Jun‐13 Sample  Type N FD N N N N N N N N SS N N N N N N N N N N N N FD N N N N N N N N N N Start  Depth  (ft) 9 5 0 0.5 5 0 0.5 0 0.5 5 5 9 0.5 4 5 0 5 0 0.5 5 0 0.5 5 0 0 0.5 5 0 3.5 0 0.5 5 0 0.5 End  Depth  (ft) 10 6 0.5 1.5 6 0.5 1.5 0.5 1.5 6 6 10 1.5 5 6 0.5 6 0.5 1.5 6 0.5 1.5 6 0.5 0.5 1.5 6 0.5 4 0.5 1.5 6 0.5 1.5 Plants ‐‐ ‐‐ x x ‐‐ x x x x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ x ‐‐ x x ‐‐ x x ‐‐ x x x ‐‐ x ‐‐ x x ‐‐ x x Inverteb rates ‐‐ ‐‐ x x ‐‐ x x x x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ x ‐‐ x x ‐‐ x x ‐‐ x x x ‐‐ x ‐‐ x x ‐‐ x x Birds ‐‐ ‐‐ x x ‐‐ x x x x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ x ‐‐ x x ‐‐ x x ‐‐ x x x ‐‐ x ‐‐ x x ‐‐ x x Burrowing  Mammals Mammals ‐‐ ‐‐ ‐‐ x x x x x ‐‐ x x x x x x x x x ‐‐ x ‐‐ x ‐‐ ‐‐ x x ‐‐ x ‐‐ x x x ‐‐ x x x x x ‐‐ x x x x x ‐‐ x x x x x x x ‐‐ x x x ‐‐ x x x x x ‐‐ x x x x x PAGE 4 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID ELBS2025 ELBS2026 ELBS2026 ELBS2026 ELBS2028 ELBS2028 ELBS2028 ELBS2034 ELBS2035 ELBS2035 ELBS2035 ELBS2036 ELBS2036 ELBS2036 ELBS3000 ELBS3001 ELBS3002 ELBS3002 ELBS3002 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3003 ELBS3004 ELBS3005 ELBS3006 ELBS3007 ELBS3007 ELBS3007 ELBS3007 ELBS3008 ELBS3009 ELBS3009 EN0411151012BAO  Sample ID ELBS2025S003 ELBS2026S001 ELBS2026S002 ELBS2026S003 ELBS2028S001 ELBS2028S002 ELBS2028S003 ELBS2034S001 ELBS2035S001 ELBS2035S002 ELBS2035S003 ELBS2036S001 ELBS2036S002 ELBS2036S003 ELBS3000S001 ELBS3001S001 ELBS3002S001 ELBS3002S002 ELBS3002S003 ELBS3003S001 ELBS3003S001SP ELBS3003S002 ELBS3003S003 ELBS3003S004 ELBS3004S001 ELBS3005S001 ELBS3006S001 ELBS3007D003 ELBS3007S001 ELBS3007S002 ELBS3007S003 ELBS3008S001 ELBS3009S001 ELBS3009S002 Sample Date 14‐Jun‐13 11‐Jun‐13 11‐Jun‐13 11‐Jun‐13 11‐Jun‐13 11‐Jun‐13 11‐Jun‐13 20‐Jun‐13 19‐Jun‐13 19‐Jun‐13 19‐Jun‐13 20‐Jun‐13 20‐Jun‐13 20‐Jun‐13 14‐May‐14 13‐May‐14 20‐May‐14 20‐May‐14 20‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 14‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 Sample  Type N N N N N N N N N N N N N N N N N N N N SS N N N N N N FD N N N N N N Start  Depth  (ft) 5 0 0.5 5 0 5 8.5 14.5 0 5.5 9.5 0 5.5 9.5 0 0.5 0.5 5 9 0 0 0.5 5 9 0.5 0.5 5 5 0 0.5 5 9.2 0 5 End  Depth  (ft) 6 0.5 1.5 6 0.5 6 9 15.5 0.5 6.5 10.5 0.5 6.5 10.5 0.5 1.5 1.5 6 10 0.5 0.5 1.5 6 10 1.5 1.5 6 6 0.5 1 6 9.8 0.5 6 Plants ‐‐ x x ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ x ‐‐ ‐‐ x x x ‐‐ ‐‐ x x x ‐‐ ‐‐ x x ‐‐ ‐‐ x x ‐‐ ‐‐ x ‐‐ Inverteb rates ‐‐ x x ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ x ‐‐ ‐‐ x x x ‐‐ ‐‐ x x x ‐‐ ‐‐ x x ‐‐ ‐‐ x x ‐‐ ‐‐ x ‐‐ Birds ‐‐ x x ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ x ‐‐ ‐‐ x x x ‐‐ ‐‐ x x x ‐‐ ‐‐ x x ‐‐ ‐‐ x x ‐‐ ‐‐ x ‐‐ Burrowing  Mammals Mammals ‐‐ x x x x x ‐‐ x x x ‐‐ x ‐‐ ‐‐ ‐‐ ‐‐ x x ‐‐ ‐‐ ‐‐ ‐‐ x x ‐‐ ‐‐ ‐‐ ‐‐ x x x x x x ‐‐ x ‐‐ ‐‐ x x x x x x ‐‐ x ‐‐ ‐‐ x x x x ‐‐ x ‐‐ x x x x x ‐‐ x ‐‐ ‐‐ x x ‐‐ x PAGE 5 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID ELBS3010 ELBS3010 ELBS3011 ELBS3011 ELBS3012 ELBS3012 ELBS3015 ELBS3015 ELBS3016 ELBS3016 ELBS3017 ELBS3020 ELBS3020 ELBS3021 ELBS3021 ELBS3022 ELBS3023 ELBS3023 ELBS3024 ELBS3024 ELSS01 GMBS2012A GMBS2012B GMBS2012B MH02072993 STBS1019 STBS3008 STBS3008 SWBS1006 SWBS1006 Soil Vapor ELSV01 ELSV02 ELSV03 EN0411151012BAO  Sample ID ELBS3010S001 ELBS3010S002 ELBS3011S001 ELBS3011S002 ELBS3012S001 ELBS3012S002 ELBS3015S001 ELBS3015S002 ELBS3016S001 ELBS3016S001SP ELBS3017S001 ELBS3020S001 ELBS3020S002 ELBS3021S001 ELBS3021S002 ELBS3022S001 ELBS3023S001 ELBS3023S001SP ELBS3024S001 ELBS3024S002 EL1S1 GMBS2012AS001 GMBS2012BS001 GMBS2012BS001SP 072993MH02 STBS1019S001 STBS3008S001 STBS3008S002 SWBS1006S001 SWBS1006S002 RV434 RV486 RV487 Sample Date 20‐May‐14 20‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 14‐May‐14 14‐May‐14 13‐May‐14 13‐May‐14 13‐May‐14 17‐Jun‐14 17‐Jun‐14 17‐Jun‐14 17‐Jun‐14 17‐Jun‐14 17‐Jun‐14 17‐Jun‐14 23‐May‐96 27‐Jan‐14 27‐Jan‐14 27‐Jan‐14 29‐Jul‐93 22‐May‐12 15‐May‐14 15‐May‐14 16‐Sep‐08 16‐Sep‐08 Sample  Type N N N N N N N N N SS N N N N N N N SS N N N N N SS N N N N N N Start  Depth  (ft) 0 0.5 0.5 5 0 5 0 5 0 0 0 0 0.5 1 3 1 0 0 0 3 0 0.7 0.6 0.6 0 1 0 5 5.5 9.5 End  Depth  (ft) 0.5 1.5 1.5 6 0.5 6 0.5 5.5 0.5 0.5 0.5 0.5 1.5 1.5 3.5 1.5 0.5 0.5 0.5 3.5 0.5 1.2 1.1 1.1 0 1.5 0.5 6 6.5 10.5 Plants x x x ‐‐ x ‐‐ x ‐‐ x x x x x x ‐‐ x x x x ‐‐ x x x x x x x ‐‐ ‐‐ ‐‐ Inverteb rates x x x ‐‐ x ‐‐ x ‐‐ x x x x x x ‐‐ x x x x ‐‐ x x x x x x x ‐‐ ‐‐ ‐‐ Birds x x x ‐‐ x ‐‐ x ‐‐ x x x x x x ‐‐ x x x x ‐‐ x x x x x x x ‐‐ ‐‐ ‐‐ 11‐Jul‐97 17‐Jul‐97 17‐Jul‐97 N N N 5 6 4 5 6 4 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Burrowing  Mammals Mammals x x x x x x ‐‐ x x x ‐‐ x x x ‐‐ x x x x x x x x x x x x x ‐‐ x x x x x x x x x ‐‐ x x x x x x x x x x x x x x x ‐‐ x ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ x x x PAGE 6 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID ELSV03 ELSV08 ELSV1003 ELSV1004 ELSV1004 ELSV1004 ELSV1400 ELSV1400 ELSV1401 ELSV1401 ELSV1402 ELSV1402 ELSV1403 ELSV1403 ELSV2000 ELSV2001 ELSV2001 ELSV2002 ELSV2003 ELSV2004 ELSV2006 ELSV2006 ELSV2008 ELSV2009 ELSV2011 ELSV2012 ELSV2013 ELSV2014 ELSV2016 ELSV2018 ELSV3000 SWSV1006 SWSV1006 EN0411151012BAO  Sample ID RV488 RV733 ELSV1003S050 ELSV1004D050 ELSV1004S050 ELSV1004S100 ELSV1400S01 ELSV1400S02 ELSV1401S01 ELSV1401S02 ELSV1402S01 ELSV1402S02 ELSV1403S01 ELSV1403S02 ELSV2000S001 ELSV2001S001 ELSV2001S002 ELSV2002S001 ELSV2003S001 ELSV2004S001 ELSV2006S001 ELSV2006S001SP ELSV2008S001 ELSV2009S001 ELSV2011S001 ELSV2012S001 ELSV2013S001 ELSV2014S001 ELSV2016S001 ELSV2018S001 ELSV3000S001 SWSV1006S001 SWSV1006S002 Sample Date 17‐Jul‐97 29‐Sep‐99 26‐Mar‐08 26‐Mar‐08 26‐Mar‐08 26‐Mar‐08 28‐Apr‐08 28‐Apr‐08 28‐Apr‐08 28‐Apr‐08 16‐May‐08 16‐May‐08 16‐May‐08 16‐May‐08 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 07‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 07‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 05‐Aug‐13 23‐May‐14 25‐Sep‐08 25‐Sep‐08 Sample  Type N N N FD N N N N N N N N N N N N N N N N N SS N N N N N N N N N N N Start  Depth  (ft) 8 5 4 4 4 9 4 9 4 9 4 9 4 8.5 5 5 9.3 5 5 5 5 5 9.5 5 5 5 5 5 5 5 5 4 9 End  Depth  (ft) 8 5 5 5 5 10 5 10 5 10 5 10 5 9.5 5.5 5.5 9.8 5.5 5.5 5.5 5.5 5.5 10 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5.5 5 10 Plants ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Inverteb rates ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Birds ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Burrowing  Mammals Mammals ‐‐ ‐‐ ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ ‐‐ ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ x ‐‐ ‐‐ PAGE 7 OF 8 ATTACHMENT 1, TABLE 2 Summary of Samples Used in the Ecological Risk Assessment RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Location ID Sample ID Sample Date Notes: ‐‐ = not used FD = field duplicate ft = feet N = primary sample SS = split sample X = Sample results used for this exposure scenario EN0411151012BAO  Sample  Type Start  Depth  (ft) End  Depth  (ft) Plants Inverteb rates Birds Burrowing  Mammals Mammals PAGE 8 OF 8 ATTACHMENT 1, TABLE 3 Detected Analytes in Media of Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Soil Soil Soil Soil Vapor (0 to 2 feet bgs) (0 to 4 feet bgs) (0 to 6 feet bgs) (0 to 6 feet bgs) Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Perchlorate Phosphate Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin EN0411151012BAO  Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Perchlorate Phosphate Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Perchlorate Phosphate Selenium Silver Strontium Thallium Tin Titanium Vanadium Zinc Zirconium 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Benzene Chloroform Dichlorodifluoromethane Ethylbenzene Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Xylenes, Total PAGE 1 OF 3 ATTACHMENT 1, TABLE 3 Detected Analytes in Media of Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Soil Soil Soil Soil Vapor (0 to 2 feet bgs) (0 to 4 feet bgs) (0 to 6 feet bgs) (0 to 6 feet bgs) 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1‐Methyl naphthalene 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid 2‐Methylnaphthalene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Acenaphthene Acenaphthylene Anthracene Aroclor‐1254 Aroclor‐1260 Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene beta‐BHC bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Chrysene Dibenzo(a,h)anthracene Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde EN0411151012BAO  1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1‐Methyl naphthalene 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid 2‐Methylnaphthalene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Acenaphthene Acenaphthylene Anthracene Aroclor‐1254 Aroclor‐1260 Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene beta‐BHC bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Chrysene Dibenzo(a,h)anthracene Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1‐Methyl naphthalene 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid 2‐Methylnaphthalene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Acenaphthene Acenaphthylene Acetone Anthracene Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene beta‐BHC bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Chrysene Dibenzo(a,h)anthracene Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Endosulfan I PAGE 2 OF 3 ATTACHMENT 1, TABLE 3 Detected Analytes in Media of Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Soil Soil Soil Soil Vapor (0 to 2 feet bgs) (0 to 4 feet bgs) (0 to 6 feet bgs) (0 to 6 feet bgs) Fluoranthene Fluorene Heptachlor epoxide Indeno(1,2,3‐cd)pyrene MCPA Methylene chloride Mirex Naphthalene Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Phenanthrene Pyrene Styrene Xylenes, Total EN0411151012BAO  Fluoranthene Fluorene Heptachlor epoxide Indeno(1,2,3‐cd)pyrene MCPA Methylene chloride Mirex m‐Xylene & p‐Xylene Naphthalene Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Phenanthrene Pyrene Styrene Xylenes, Total Endosulfan sulfate Endrin Endrin aldehyde Ethylbenzene Fluoranthene Fluorene Heptachlor Heptachlor epoxide Indeno(1,2,3‐cd)pyrene MCPA Methylene chloride Mirex Naphthalene Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin Phenanthrene Pyrene Silvex Styrene Xylenes, Total PAGE 3 OF 3 ATTACHMENT 1, TABLE 4 Summary Statistics for Detected Analytes RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California 14  Depth   Matrix Interval Measured Data Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO  0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft Type I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O  EcoRAClass Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Preferred Analyte Name 15 16 17 18 19 20 Qualifier of  Depth of  Location of    Minimum  Maximum  Maximum  Maximum  Maximum  Detected  Detected  Detected  SQL for   Minimum  Maximum  SQL for   Number   Number  Concentratio Concentratio Concentratio  Arithmetic  Non‐ Non‐ of   Frequency   Percent  Detected  Detected  of  n Mean Value n n detects detects Value Value  Units Detects Analyses of Detects Detects Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Phosphate Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene  mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg  2 40 20 49 42 38 21 41 40 40 41 12 10 38 37 23 16 36 40 6 9 4 14 27 35 4 35 4 40 40 36 14 2 23 22 12 18 15 21 15 20 13 11 14 16 10 8 12 23 23 23 22 2 1 13 12 17 12 6 19 4 7 13 2 2 2 3 7 14 2 10 40 42 52 42 40 38 43 40 40 41 21 19 40 37 23 25 40 40 10 9 19 20 40 43 4 40 4 40 40 37 20 20 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 23 9 9 31 31 31 31 28 31 31 31 31 31 31 31 31 31 31 31  2/10   40/40   20/42   49/52   42/42   38/40   21/38   41/43   40/40   40/40   41/41   12/21   10/19   38/40   37/37   23/23   16/25   36/40   40/40   6/10   9/9   4/19   14/20   27/40   35/43   4/4   35/40   4/4   40/40   40/40   36/37   14/20   2/20   23/23   22/23   12/23   18/23   15/23   21/23   15/23   20/23   13/23   11/23   14/23   16/23   10/23   8/23   12/23   23/23   23/23   23/23   22/23   2/9   1/9   13/31   12/31   17/31   12/31   6/28   19/31   4/31   7/31   13/31   2/31   2/31   2/31   3/31   7/31   14/31   2/31  20 100 48 94 100 95 55 95 100 100 100 57 53 95 100 100 64 90 100 60 100 21 70 68 81 100 88 100 100 100 97 70 10 100 96 52 78 65 91 65 87 57 48 61 70 43 35 52 100 100 100 96 22 11 42 39 55 39 21 61 13 23 42 6 6 6 10 23 45 6 0.0039 4440 0.122 0.73 61 0.16 1.1 0.035 6 1.8 4.5 0.2 0.56 1.8 8.5 217 0.0025 0.27 3 0.78 0.65 0.52 0.16 0.11 0.0297 18.2 0.097 709 18 15 0.78 0.0047 0.00208 3.6E‐07 3.88E‐07 1.42E‐06 8.41E‐08 1.87E‐07 3.11E‐07 1.74E‐07 4.61E‐07 1.55E‐07 4.38E‐07 3.97E‐07 1.27E‐07 2.01E‐07 4.96E‐08 9.8E‐08 6.51E‐10 4.47E‐09 2.91E‐06 1.41E‐06 0.018 0.94 0.0002 0.00023 0.00043 0.00025 0.00097 0.00033 0.00093 0.00093 0.00036 0.00094 0.0012 0.00051 0.00048 0.00037 0.00045 0.00089 0.024 33200 7.5 110 189 1.3 9.99 0.751 32.9 12.7 25.6 3.1 3.2 16.5 33.6 887 0.033 0.961 24.7 3.3 7.8 0.82 1 0.39 3.5 31.5 0.419 1320 58.9 126 5.74 0.099 0.046 0.00149 0.000181 0.0000157 0.0000191 7.03E‐06 0.0000617 7.73E‐06 0.0000416 1.84E‐06 0.0000098 0.0000102 0.0000109 2.81E‐06 0.0000011 2.29E‐06 0.000025 0.0000519 0.0428 0.000642 0.032 0.94 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.0012 0.0015 0.017 0.0021 0.13 2.3 0.015 0.0082 NA  0.173 10 NA  0.06 1.87 0.8 NA  NA  NA  0.8 0.34 8.4 NA  NA  0.0114 1.03 NA  0.604 NA  0.604 0.22 0.204 0.0522 NA  0.5 NA  NA  NA  1.56 0.0326 0.00712 NA  1.44E‐07 8.56E‐08 5.66E‐08 9.44E‐08 1.2E‐07 8E‐08 1.41E‐07 1.67E‐07 6.12E‐08 1.55E‐07 7.44E‐08 5.96E‐08 3.72E‐08 2.82E‐08 NA  NA  NA  4.52E‐07 0.0107 2.14 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.012 NA 20 12 NA 2 20 2 NA NA NA 11 10 10 NA NA 0.4 20 NA 2 NA 11 6.92 15 2 NA 10 NA NA NA 1.56 0.106 0.106 NA 1.44E‐07 3.12E‐06 7.22E‐07 5.28E‐07 1.14E‐06 0.0000015 8.88E‐07 2.36E‐06 6.82E‐06 1.82E‐06 6.56E‐07 2.16E‐06 1.02E‐06 3.8E‐07 NA NA NA 4.52E‐07 0.05 5.6 0.8 0.042 0.042 0.042 0.042 0.042 0.042 0.8 0.042 0.8 0.8 0.8 0.8 0.8 0.8 0.8 ELBS2020  ELBS2003  ELSS01  ELBS05  ELBS2022  ELBS1027  ELBS2000  ELBS3000  ELBS2003  ELBS2022  ELBS2009  ELBS2009  ELBS2002  ELBS2000  ELBS2003  ELBS2022  ELBS1021  GMBS2012  ELBS2003  ELBS1017  ELBS2000  ELBS1014  ELBS1016  ELBS1014  ELBS1019  ELBS2007  ELBS2021  GMBS2012  ELBS2003  ELBS2024  ELBS2003  ELBS3000  ELBS3003  ELBS2012  ELBS3023  ELBS3023  ELBS2012  ELBS3012  ELBS3023  ELBS3012  ELBS2012  ELBS3023  ELBS2012  ELBS3003  ELBS3012  ELBS3012  ELBS2012  ELBS3003  ELBS2012  ELBS2012  ELBS2012  ELBS2009  ELBS2009  ELBS2000  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  GMBS2012A  GMBS2012A  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  1.5 0.5 0.5 0.5 0.5 1 0.5 0.5 0.5 0.5 0.5 0.5 1.5 0.5 0.5 0.5 1 1.2 0.5 1 0.5 1 1 1 1 0.5 0.5 1.2 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.2 1.2 1.5 1.5 1.5 1.5 1.5 J  =  J  J  =  =  =  =  =  J  =  J  =  J  =  J  =  =  =  J  J  J  J  J  J  =  J  =  =  =  =  =  =  =  =  =  =  =  =  =  =  J  =  =  =  J  =  =  =  =  =  =  =  J  =  =  =  =  =  =  =  =  =  J  J  =  =  =  =  J  0.00591 16800 0.482 13 113 0.732 3.39 0.227 20 6.68 12.2 1.27 0.843 8.35 19.2 375 0.0103 0.511 14.2 1.12 2.9 0.574 0.519 0.196 0.196 NA  0.269 NA  41.3 51.8 3.39 0.0343 0.00452 0.000336 0.0000425 0.00000303 0.00000396 0.00000173 0.0000123 0.00000171 0.00000907 0.000000529 0.00000194 0.00000161 0.00000225 0.00000051 0.000000199 0.000000436 0.00000598 0.0000107 0.00544 0.000127 0.0202 NA  0.0407 0.0257 0.0361 0.0095 0.0206 0.0522 0.00458 0.0103 0.0846 0.00107 0.00135 0.00123 0.00113 0.0051 0.0783 0.0015 21  Standard  Deviation 0.00603 6220 1.14 21.9 24.3 0.244 2.68 0.149 6.39 2.07 4.5 0.784 0.652 2.8 5.78 136 0.00671 0.143 4.71 0.78 2.4 0.0777 0.275 0.0749 0.549 NA  0.0794 NA  8.59 18.8 1.24 0.0304 0.0101 0.000435 0.0000515 0.00000401 0.00000491 0.00000204 0.000016 0.00000217 0.0000107 0.000000464 0.00000265 0.0000023 0.00000301 0.00000067 0.000000272 0.000000571 0.00000745 0.0000139 0.00922 0.000165 0.00884 NA  0.212 0.13 0.176 0.0404 0.0961 0.264 0.0168 0.0464 0.441 0.00013 0.00015 0.00336 0.000701 0.0232 0.406 0.00288 22 23   Recommend ed UCL  Recommended UCL Basis 0.015 18400 0.791 26.4 120 0.799 4.2 0.267 21.7 7.24 13.4 1.64 1.13 9.12 20.8 424 0.0129 0.551 15.5 1.62 4.39 0.625 0.646 0.219 0.569  NA  0.292  NA  43.6 56.9 3.74 0.0473 0.0379 0.000677 0.0000905 0.00000453 0.00000577 0.00000249 0.0000271 0.00000252 0.000013 0.000000714 0.00000295 0.00000248 0.00000336 0.000000767 0.000000308 0.00000065 0.0000117 0.000021 0.0112 0.00028 0.0337 3.26 0.434 0.179 0.36 0.0568 0.219 0.538 0.0105 0.0675 0.905 0.00129 0.0016 0.0111 0.00197 0.0507 0.831 0.0068 95% Chebyshev UCL* 95% Student's‐t UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (Chebyshev) UCL Fewer Than Five Samples 95% KM (t) UCL Fewer Than Five Samples 95% Student's‐t UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% Adjusted Gamma UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Percentile Bootstrap) 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Adjusted Gamma UCL 95% Adjusted Gamma UCL 95% Adjusted Gamma UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% Chebyshev UCL* 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 24 RME EPC 0.015 18400 0.791 26.4 120 0.799 4.2 0.267 21.7 7.24 13.4 1.64 1.13 9.12 20.8 424 0.0129 0.551 15.5 1.62 4.39 0.625 0.646 0.219 0.569 31.5 0.292 1320 43.6 56.9 3.74 0.0473 0.0379 0.000677 0.0000905 0.00000453 0.00000577 0.00000249 0.0000271 0.00000252 0.000013 0.000000714 0.00000295 0.00000248 0.00000336 0.000000767 0.000000308 0.00000065 0.0000117 0.000021 0.0112 0.00028 0.032 0.94 0.434 0.179 0.36 0.0568 0.219 0.538 0.0105 0.0675 0.905 0.0012 0.0015 0.0111 0.00197 0.0507 0.831 0.0068 25 RME EPC Basis 95% Chebyshev UCL* 95% Student's‐t UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (Chebyshev) UCL Maximum Result 95% KM (t) UCL Maximum Result 95% Student's‐t UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% Adjusted Gamma UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Percentile Bootstrap) 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Adjusted Gamma UCL 95% Adjusted Gamma UCL 95% Adjusted Gamma UCL 95% KM (Chebyshev) UCL Maximum Result Maximum Result 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 97.5% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL Maximum Result Maximum Result 99% KM (Chebyshev) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 99% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL PAGE 1 OF 5 ATTACHMENT 1, TABLE 4 Summary Statistics for Detected Analytes RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California 14  Matrix  Depth  Interval Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft O O O O O O O O O O O O O O O O O O O O I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I O O O O O O O O O O O O O O O O O O O O EN0411151012BAO   EcoRAClass PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC VOC VOC VOC Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Preferred Analyte Name 15 16 17 18 19 20 Qualifier of  Depth of  Location of    Minimum  Maximum  Maximum  Maximum  Maximum  Detected  Detected  Detected  SQL for   Minimum  Maximum  SQL for   Number   Number  Concentratio Concentratio Concentratio  Arithmetic  Non‐ Non‐ of   Frequency   Percent  Detected  Detected  of  n Mean Value n n detects detects Value Value  Units Detects Analyses of Detects Detects  Standard  Deviation Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex beta‐BHC Butyl benzyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Diethyl phthalate bis(2‐Ethylhexyl) phthalate Methylene chloride Styrene Xylenes, Total Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Phosphate Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium Aroclor‐1254 Aroclor‐1260 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzo‐p‐dioxin  mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg  0.000487 0.16 0.000725 0.000858 0.00487 NA  NA  NA  0.000315 NA  0.00109 NA  0.00501 0.000525 0.017 NA  NA  NA  0.000181 NA  0.006 6370 1.11 21.3 24.6 0.251 2.66 0.146 7.08 2.1 4.69 0.784 0.632 2.85 8.1 131 0.0067 0.144 5.93 0.78 2.4 0.0777 0.275 0.0729 0.537 NA  0.0813 NA  9.78 19.9 1.43 0.0304 0.0101 0.00043 5.11 3.97 4.86 2.02 1.58 2.14 1.06 4.61 2.62 2.28 2.97 6.63 2.67 5.65 0.00000739 0.0000138 0.00908 10 14 2 6 9 1 1 1 2 1 4 1 4 3 3 1 1 1 6 1 2 42 20 51 44 40 21 43 43 42 43 12 11 40 39 25 16 38 42 6 9 4 14 28 37 4 37 4 42 42 38 14 2 24 23 12 19 15 21 15 20 13 11 14 16 10 8 12 24 24 24 31 31 13 13 13 13 13 13 13 13 13 13 31 31 31 31 31 19 17 19 10 42 44 55 44 42 40 45 43 42 43 21 20 42 39 25 25 42 42 10 9 19 20 42 45 4 42 4 42 42 39 20 20 24 24 24 24 24 24 24 24 24 24 24 24 24 24 24 24 24 24  10/31   14/31   2/13   6/13   9/13   1/13   1/13   1/13   2/13   1/13   4/13   1/13   4/31   3/31   3/31   1/31   1/31   1/19   6/17   1/19   2/10   42/42   20/44   51/55   44/44   40/42   21/40   43/45   43/43   42/42   43/43   12/21   11/20   40/42   39/39   25/25   16/25   38/42   42/42   6/10   9/9   4/19   14/20   28/42   37/45   4/4   37/42   4/4   42/42   42/42   38/39   14/20   2/20   24/24   23/24   12/24   19/24   15/24   21/24   15/24   20/24   13/24   11/24   14/24   16/24   10/24   8/24   12/24   24/24   24/24   24/24  32 45 15 46 69 8 8 8 15 8 31 8 13 10 10 3 3 5 35 5 20 100 45 93 100 95 53 96 100 100 100 57 55 95 100 100 64 90 100 60 100 21 70 67 82 100 88 100 100 100 97 70 10 100 96 50 79 63 88 63 83 54 46 58 67 42 33 50 100 100 100 0.00042 0.00079 0.00035 0.0004 0.00053 0.00055 0.00055 0.0005 0.00047 0.00047 0.0004 0.00073 0.00073 0.0011 0.0044 0.00597 0.0287 0.0027 0.000234 0.000372 0.0039 4440 0.122 0.73 61 0.16 1.1 0.035 6 1.8 4.5 0.2 0.5 1.8 8.5 217 0.0025 0.27 3 0.78 0.65 0.52 0.16 0.11 0.0297 18.2 0.097 709 18 15 0.78 0.0047 0.00208 3.6E‐07 3.88E‐07 1.42E‐06 8.41E‐08 1.87E‐07 3.11E‐07 1.74E‐07 4.61E‐07 1.55E‐07 4.38E‐07 3.97E‐07 1.27E‐07 2.01E‐07 4.96E‐08 9.8E‐08 6.51E‐10 4.47E‐09 2.91E‐06 0.0022 0.91 0.0018 0.0029 0.019 0.00055 0.00055 0.0005 0.0011 0.00047 0.0047 0.00073 0.013 0.0023 0.099 0.00597 0.0287 0.0027 0.000723 0.000372 0.024 33200 7.5 110 189 1.3 9.99 0.751 38.5 12.7 25.6 3.1 3.2 16.5 53.4 887 0.033 0.961 32.2 3.3 7.8 0.82 1 0.39 3.5 31.5 0.419 1320 73 126 8.19 0.099 0.046 0.00149 0.000181 0.0000157 0.0000191 7.03E‐06 0.0000617 7.73E‐06 0.0000416 1.84E‐06 0.0000098 0.0000102 0.0000109 2.81E‐06 0.0000011 2.29E‐06 0.000025 0.0000519 0.0428 0.0034 0.0034 0.00284 0.00284 0.00284 0.00142 0.00284 0.00284 0.00284 0.00142 0.00142 0.00142 0.0342 0.0342 0.0342 0.0342 0.0342 0.0084 0.0034 0.0034 0.0082 NA  0.173 10 NA  0.06 1.87 0.8 NA  NA  NA  0.8 0.34 8.4 NA  NA  0.0114 1.03 NA  0.604 NA  0.604 0.22 0.204 0.0522 NA  0.5 NA  NA  NA  1.56 0.0326 0.00712 NA  1.44E‐07 8.56E‐08 5.66E‐08 9.44E‐08 1.2E‐07 8E‐08 1.41E‐07 1.67E‐07 6.12E‐08 1.1E‐07 7.44E‐08 5.96E‐08 3.72E‐08 2.82E‐08 NA  NA  NA  0.8 0.8 0.034 0.034 0.004 0.0166 0.034 0.034 0.034 0.0166 0.004 0.02 0.36 0.8 0.36 0.8 0.8 0.044 0.012 0.012 0.012 NA 20 12 NA 2 20 2 NA NA NA 11 10 10 NA NA 0.4 20 NA 2 NA 11 6.92 15 2 NA 10 NA NA NA 1.56 0.106 0.106 NA 1.44E‐07 3.12E‐06 7.22E‐07 5.28E‐07 1.39E‐06 0.0000015 8.88E‐07 2.36E‐06 6.82E‐06 1.82E‐06 6.56E‐07 2.16E‐06 1.02E‐06 3.8E‐07 NA NA NA ELBS2004  ELBS2007  ELBS2012  ELBS2012  ELBS2022  ELBS2009  ELBS2012  ELBS2012  ELBS2000  ELBS2009  ELBS2022  ELBS2000  ELBS1012  ELBS1027  ELBS1012  ELBS1020  ELBS1013  ELBS1013  ELBS1019  ELBS1019  ELBS2020  ELBS2003  ELSS01  ELBS05  ELBS2022  ELBS1027  ELBS2000  ELBS3000  ELBS2023  ELBS2022  ELBS2009  ELBS2009  ELBS2002  ELBS2000  ELBS2023  ELBS2022  ELBS1021  GMBS2012  ELBS2023  ELBS1017  ELBS2000  ELBS1014  ELBS1016  ELBS1014  ELBS1019  ELBS2007  ELBS2021  GMBS2012  ELBS2023  ELBS2024  ELBS2023  ELBS3000  ELBS3003  ELBS2012  ELBS3023  ELBS3023  ELBS2012  ELBS3012  ELBS3023  ELBS3012  ELBS2012  ELBS3023  ELBS2012  ELBS3003  ELBS3012  ELBS3012  ELBS2012  ELBS3003  ELBS2012  ELBS2012  ELBS2012  1.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1.5 0.5 0.5 0.5 0.5 1 0.5 0.5 4 0.5 0.5 0.5 1.5 0.5 4 0.5 1 1.2 4 1 0.5 1 1 1 1 0.5 0.5 1.2 4 0.5 4 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 =  =  J  J  J  J  J  J  J  J  J  J  J  J  J  J  =  J  J  =  J  =  J  J  =  =  =  =  =  J  =  J  =  J  =  J  =  =  J  J  J  J  J  J  J  =  J  =  =  =  =  =  =  =  =  =  =  =  =  =  =  J  =  =  =  J  =  =  =  =  =  0.00133 0.0322 0.00108 0.00139 0.00372 NA  NA  NA  0.000785 NA  0.00112 NA  0.00441 0.00157 0.0102 NA  NA  NA  0.000406 NA  0.0059 17000 0.466 12.7 115 0.738 3.36 0.224 20.8 6.79 12.5 1.27 0.835 8.42 20.4 379 0.0103 0.503 15 1.12 2.9 0.574 0.519 0.196 0.191 NA  0.275 NA  42.2 53.2 3.53 0.0343 0.0045 0.000323 4.08 2.9 3.81 1.66 1.18 1.65 8.71 5.09 1.86 1.53 2.16 4.9 1.92 4.2 0.00000573 0.0000102 0.00522 21 22 23   Recommend ed UCL  Recommended UCL Basis 0.00161 0.219 0.00823 0.00205 0.00637 0.00392 0.00801 0.00801 0.00135 0.00391 0.00184 0.00472 0.00932 0.0022 0.0176 0.0976 0.0962 0.0101 0.000548 0.00476 0.015 18700 0.76 25.4 121 0.805 4.15 0.266 22.7 7.34 13.7 1.64 1.1 9.18 22.6 424 0.0129 0.542 16.6 1.62 4.39 0.625 0.646 0.22 0.547  NA  0.297  NA  44.8 58.4 3.92 0.0473 0.0379 6.4 8.73 4.35 5.55 2.4 2.62 2.42 1.25 6.88 2.84 2.36 3.23 7.37 2.96 6.27 1.12 2 0.0106 95% KM (t) UCL 97.5% KM (Chebyshev) UCL 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (BCA) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 95% Chebyshev UCL* 95% KM (t) UCL 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL*  95% Student's‐t UCL   95% KM (t) UCL   95% KM (Chebyshev) UCL   95% Adjusted Gamma UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (BCA) UCL   95% Student's‐t UCL   95% Student's‐t UCL   95% Student's‐t UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% Student's‐t UCL   95% Adjusted Gamma UCL   95% KM (t) UCL   95% KM (t) UCL   95% Student's‐t UCL   95% KM (t) UCL   95% Student's‐t UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (BCA) UCL   95% KM (Chebyshev) UCL   Fewer Than Five Samples   95% KM (t) UCL   Fewer Than Five Samples   95% Student's‐t UCL   95% Student's‐t UCL   95% KM (t) UCL   95% KM (t) UCL   99% KM (Chebyshev) UCL   95% Adjusted Gamma UCL   95% KM (Chebyshev) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (Chebyshev) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL   95% Adjusted Gamma UCL   95% Adjusted Gamma UCL   95% Adjusted Gamma UCL  24 RME EPC 0.00161 0.219 0.0018 0.00205 0.00637 0.00055 0.00055 0.0005 0.0011 0.00047 0.00184 0.00073 0.00932 0.0022 0.0176 0.00597 0.0287 0.0027 0.000548 0.000372 0.015 18700 0.76 25.4 121 0.805 4.15 0.266 22.7 7.34 13.7 1.64 1.1 9.18 22.6 424 0.0129 0.542 16.6 1.62 4.39 0.625 0.646 0.22 0.547 31.5 0.297 1320 44.8 58.4 3.92 0.0473 0.0379 0.00149 0.000181 0.0000157 0.0000191 0.00000703 0.0000617 0.00000773 0.0000416 0.00000184 0.0000098 0.0000102 0.0000109 0.00000281 0.0000011 0.00000229 0.000025 0.0000519 0.0106 25 RME EPC Basis 95% KM (t) UCL 97.5% KM (Chebyshev) UCL Maximum Result 95% KM (t) UCL 95% KM (BCA) UCL Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result 95% KM (t) UCL Maximum Result 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL Maximum Result Maximum Result Maximum Result 95% KM (t) UCL Maximum Result 95% Chebyshev UCL* 95% Student's‐t UCL  95% KM (t) UCL  95% KM (Chebyshev) UCL  95% Adjusted Gamma UCL  95% KM (t) UCL  95% KM (t) UCL  95% KM (BCA) UCL  95% Student's‐t UCL  95% Student's‐t UCL  95% Student's‐t UCL  95% KM (t) UCL  95% KM (t) UCL  95% KM (t) UCL  95% Student's‐t UCL  95% Adjusted Gamma UCL  95% KM (t) UCL  95% KM (t) UCL  95% Student's‐t UCL  95% KM (t) UCL  95% Student's‐t UCL  95% KM (t) UCL  95% KM (t) UCL  95% KM (BCA) UCL  95% KM (Chebyshev) UCL  Maximum Result  95% KM (t) UCL  Maximum Result  95% Student's‐t UCL  95% Student's‐t UCL  95% KM (t) UCL  95% KM (t) UCL  99% KM (Chebyshev) UCL  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  95% Adjusted Gamma UCL  PAGE 2 OF 5 ATTACHMENT 1, TABLE 4 Summary Statistics for Detected Analytes RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California 14  Matrix  Depth  Interval Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I EN0411151012BAO   EcoRAClass Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC VOC VOC VOC VOC Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Preferred Analyte Name 15 16 17 18 19 20 Qualifier of  Depth of  Location of    Minimum  Maximum  Maximum  Maximum  Maximum  Detected  Detected  Detected  SQL for   Minimum  Maximum  SQL for   Number   Number  Concentratio Concentratio Concentratio  Arithmetic  Non‐ Non‐ of   Frequency   Percent  Detected  Detected  of  n Mean Value n n detects detects Value Value  Units Detects Analyses of Detects Detects Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex beta‐BHC Butyl benzyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Diethyl phthalate bis(2‐Ethylhexyl) phthalate Methylene chloride Styrene Xylenes, Total m‐Xylene & p‐Xylene Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Nitrate‐NO3 Nitrite‐NO2 Phosphate Selenium Silver Strontium Thallium Tin Titanium Vanadium Zinc  mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg  23 2 1 14 12 17 13 6 22 4 7 14 2 2 2 3 7 15 2 10 15 2 6 9 1 1 1 2 1 4 1 4 3 3 1 1 1 6 1 1 4 68 29 83 72 66 34 71 69 68 69 22 14 66 65 42 26 60 68 10 15 5 18 34 60 6 62 1 6 68 68 24 9 9 34 34 34 34 31 34 34 34 34 34 34 34 34 34 34 34 34 34 13 13 13 13 13 13 13 13 13 13 32 32 32 32 32 20 18 20 19 18 68 71 87 72 68 66 73 69 68 69 35 27 68 65 42 39 68 68 15 17 32 33 68 71 6 68 6 6 68 68  23/24   2/9   1/9   14/34   12/34   17/34   13/34   6/31   22/34   4/34   7/34   14/34   2/34   2/34   2/34   3/34   7/34   15/34   2/34   10/34   15/34   2/13   6/13   9/13   1/13   1/13   1/13   2/13   1/13   4/13   1/13   4/32   3/32   3/32   1/32   1/32   1/20   6/18   1/20   1/19   4/18   68/68   29/71   83/87   72/72   66/68   34/66   71/73   69/69   68/68   69/69   22/35   14/27   66/68   65/65   42/42   26/39   60/68   68/68   10/15   15/17   5/32   18/33   34/68   60/71   6/6   62/68   1/6   6/6   68/68   68/68  96 22 11 41 35 50 38 19 65 12 21 41 6 6 6 9 21 44 6 29 44 15 46 69 8 8 8 15 8 31 8 13 9 9 3 3 5 33 5 5 22 100 41 95 100 97 52 97 100 100 100 63 52 97 100 100 67 88 100 67 88 16 55 50 85 100 91 17 100 100 100 1.41E‐06 0.018 0.94 0.0002 0.00023 0.00043 0.00025 0.00097 0.00033 0.00093 0.00093 0.00036 0.00094 0.0012 0.00051 0.00048 0.00037 0.00045 0.00089 0.00042 0.00079 0.00035 0.0004 0.00053 0.00055 0.00055 0.0005 0.00047 0.00047 0.0004 0.00073 0.00073 0.0011 0.0044 0.00597 0.0287 0.0027 0.000234 0.000372 0.000372 0.0039 4440 0.122 0.73 49.1 0.16 1.1 0.035 6 1.8 4.5 0.2 0.22 1.8 8.5 158 0.0025 0.16 3 0.78 0.44 0.52 0.16 0.11 0.0297 18.2 0.097 0.384 709 18 15 0.000642 0.032 0.94 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.0012 0.0015 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.0029 0.019 0.00055 0.00055 0.0005 0.0011 0.00047 0.0047 0.00073 0.013 0.0023 0.099 0.00597 0.0287 0.0027 0.000723 0.000372 0.000372 0.043 33200 7.5 110 230 1.9 10.1 0.751 38.5 18.5 25.6 11.2 3.2 16.5 58 887 0.033 0.961 32.2 3.3 7.8 0.82 1 0.51 3.5 41.3 0.427 0.384 1320 73 126 4.52E‐07 0.0107 2.14 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.00284 0.00284 0.00284 0.00142 0.00284 0.00284 0.00284 0.00142 0.00142 0.00142 0.0342 0.0342 0.0342 0.0342 0.0342 0.0084 0.0034 0.0034 0.0034 0.00434 NA  0.149 10 NA  0.06 1.87 0.8 NA  NA  NA  0.8 0.34 8.4 NA  NA  0.0114 0.214 NA  0.604 0.86 0.604 0.22 0.204 0.0438 NA  0.46 0.564 NA  NA  NA  4.52E‐07 0.05 5.6 0.8 0.042 0.042 0.042 0.042 0.042 0.042 0.8 0.042 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.034 0.034 0.004 0.0166 0.034 0.034 0.034 0.0166 0.004 0.02 0.36 0.8 0.36 0.8 0.8 0.044 0.012 0.012 0.012 0.012 NA 20 12 NA 2 20 2 NA NA NA 11.4 10 10 NA NA 0.4 20 NA 2 1 11.4 6.92 15 2 NA 10 7.32 NA NA NA ELBS2009  ELBS2009  ELBS2000  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  GMBS2012A  GMBS2012A  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2004  ELBS2007  ELBS2012  ELBS2012  ELBS2022  ELBS2009  ELBS2012  ELBS2012  ELBS2000  ELBS2009  ELBS2022  ELBS2000  ELBS1012  ELBS1027  ELBS1012  ELBS1020  ELBS1013  ELBS1013  ELBS1019  ELBS1019  ELBS1019  ELBS2001  ELBS2003  ELSS01  ELBS05  ELBS1016  ELBS1016  ELBS2012  ELBS3000  ELBS2023  ELBS2024  ELBS2009  ELBS2002  ELBS2002  ELBS2000  ELBS1016  ELBS2022  ELBS1021  GMBS2012  ELBS2023  ELBS1017  ELBS2000  ELBS1014  ELBS1016  ELBS1016  ELBS1019  ELBS2000  ELBS2004  ELBS2012  GMBS2012  ELBS2023  ELBS2024  0.5 0.5 0.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.2 1.2 1.5 1.5 1.5 1.5 1.5 1.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 1 1 1 1 1 1 1 1 1 6 0.5 0.5 0.5 6 6 6 0.5 4 6 0.5 6 1.5 0.5 6 0.5 1 1.2 4 1 0.5 1 1 6 1 6 6 6 1.2 4 0.5 =  =  J  =  =  =  =  =  =  =  =  =  J  J  =  =  =  =  J  =  =  J  J  J  J  J  J  J  J  J  J  J  J  J  J  =  J  J  =  J  =  =  J  J  =  =  =  =  =  =  =  J  =  J  =  J  =  =  J  J  J  J  J  J  J  =  =  J  =  =  =  1.22 0.0202 NA  0.0373 0.0236 0.0331 0.0088 0.0188 0.0477 0.0042 0.0095 0.0773 0.001 0.0013 0.0011 0.0011 0.0047 0.0715 0.0014 0.0013 0.0295 0.001 0.0013 0.0037 NA  NA  NA  7.85 NA  0.0011 NA  0.0044 0.0015 0.0101 NA  NA  NA  4.06 NA  NA  0.00748 17400 0.366 12.6 110 0.775 3.51 0.184 22.3 6.68 12 1.99 0.701 7.9 24.8 343 0.0101 0.404 16.3 1.17 2.11 0.576 0.421 0.202 0.159 27.4 0.27 NA  920 42.1 52.5 21  Standard  Deviation 1.63 0.0088 NA  0.202 0.125 0.168 0.0386 0.0915 0.253 0.016 0.0443 0.422 1.3 1.5 0.0032 7.01 0.0222 0.388 0.0027 4.87 0.153 7.25 8.58 0.0048 NA  NA  NA  3.15 NA  0.001 NA  0.005 5.25 0.0167 NA  NA  NA  1.81 NA  NA  0.00974 5810 0.884 18 28.7 0.271 2.67 0.128 6.46 2.54 4.2 2.33 0.641 2.79 10 137 0.00635 0.179 6.06 0.738 2.08 0.0637 0.269 0.084 0.431 8.02 0.0768 NA  225 9.03 17.4 22 23   Recommend ed UCL  Recommended UCL Basis 2.7 0.0337 3.26 0.396 0.163 0.329 0.0519 0.198 0.489 0.0096 0.0616 0.824 0.0012 0.0016 0.0103 0.0019 0.0462 0.757 0.0063 0.0016 0.2 0.00823 0.002 0.0061 0.00392 0.00801 0.00801 0.0013 0.00391 0.0018 0.00472 0.0093 0.0022 0.0173 0.0953 0.0939 0.00982 5.47 0.00483 0.00476 0.0121 18600 0.546 16.1 116 0.833 4.12 0.21 23.6 7.18 12.8 2.68 0.928 8.47 26.9 378 0.012 0.442 17.5 1.53 3.07 0.611 0.521 0.222 0.249 34 0.286 4.19 1110 44 56  95% KM (Chebyshev) UCL   95% KM (t) UCL  95% Chebyshev UCL*  99% KM (Chebyshev) UCL   97.5% KM (Chebyshev) UCL   99% KM (Chebyshev) UCL   97.5% KM (Chebyshev) UCL   99% KM (Chebyshev) UCL   99% KM (Chebyshev) UCL   95% KM (t) UCL   97.5% KM (Chebyshev) UCL   99% KM (Chebyshev) UCL   95% KM (t) UCL   95% KM (t) UCL   99% KM (Chebyshev) UCL   95% KM (t) UCL   99% KM (Chebyshev) UCL   99% KM (Chebyshev) UCL   97.5% KM (Chebyshev) UCL   95% KM (t) UCL   97.5% KM (Chebyshev) UCL  95% Chebyshev UCL*  95% KM (t) UCL   95% KM (BCA) UCL  95% Chebyshev UCL* 95% Chebyshev UCL* 95% Chebyshev UCL*  95% KM (t) UCL  95% Chebyshev UCL*  95% KM (t) UCL  95% Chebyshev UCL*  95% KM (t) UCL   95% KM (t) UCL   95% KM (t) UCL  95% Chebyshev UCL* 95% Chebyshev UCL* 95% Chebyshev UCL*  95% KM (t) UCL  95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Student's‐t UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Student's‐t UCL 95% Approximate Gamma UCL 95% Approximate Gamma UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% Chebyshev UCL* 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 24 25 RME EPC RME EPC Basis 0.000642 0.032 0.94 0.396 0.163 0.329 0.0519 0.198 0.489 0.0096 0.0616 0.824 0.0012 0.0015 0.0103 0.0019 0.0462 0.757 0.0063 0.0016 0.2 0.0018 0.002 0.0061 0.00055 0.00055 0.0005 0.0011 0.00047 0.0018 0.00073 0.0093 0.0022 0.0173 0.00597 0.0287 0.0027 0.000723 0.000372 0.000372 0.0121 18600 0.546 16.1 116 0.833 4.12 0.21 23.6 7.18 12.8 2.68 0.928 8.47 26.9 378 0.012 0.442 17.5 1.53 3.07 0.611 0.521 0.222 0.249 34 0.286 0.384 1110 44 56 Maximum Result  Maximum Result  Maximum Result  99% KM (Chebyshev) UCL  97.5% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  97.5% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  95% KM (t) UCL  97.5% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  95% KM (t) UCL  Maximum Result  99% KM (Chebyshev) UCL  95% KM (t) UCL  99% KM (Chebyshev) UCL  99% KM (Chebyshev) UCL  97.5% KM (Chebyshev) UCL  95% KM (t) UCL  97.5% KM (Chebyshev) UCL  Maximum Result  95% KM (t) UCL  95% KM (BCA) UCL  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  95% KM (t) UCL  Maximum Result  95% KM (t) UCL  95% KM (t) UCL  95% KM (t) UCL  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  Maximum Result  95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Student's‐t UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Student's‐t UCL 95% Approximate Gamma UCL 95% Approximate Gamma UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Adjusted Gamma UCL 95% KM (t) UCL 95% KM (t) UCL 95% Student's‐t UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Student's‐t UCL 95% KM (t) UCL Maximum Result 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL PAGE 3 OF 5 ATTACHMENT 1, TABLE 4 Summary Statistics for Detected Analytes RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California 14  Matrix  Depth  Interval Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft I O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O EN0411151012BAO   EcoRAClass Inorganics ARCL ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name 15 16 17 18 19 20 Qualifier of  Depth of  Location of    Minimum  Maximum  Maximum  Maximum  Maximum  Detected  Detected  Detected  SQL for   Minimum  Maximum  SQL for   Number   Number  Concentratio Concentratio Concentratio  Arithmetic  Non‐ Non‐ of   Frequency   Percent  Detected  Detected  of  n Mean Value n n detects detects Value Value  Units Detects Analyses of Detects Detects Zirconium Aroclor‐r1254 Aroclor‐1260 Aroclor‐5460 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzo‐p‐dioxin Octachlorodibenzofuran 2,4‐Dichlorophenoxybutyric acid MCPA Silvex Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex beta‐BHC Butyl benzyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Diethyl phthalate bis(2‐Ethylhexyl) phthalate Acetone Ethylbenzene Methylene chloride Styrene Xylenes, Total 1,1,1‐Trichloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane Benzene Chloroform Dichlorodifluoromethane Ethylbenzene  mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg   mg/kg  µg/L µg/L µg/L µg/L µg/L µg/L 61 20 3 1 35 30 14 22 18 26 17 23 14 14 15 19 11 10 12 36 36 36 30 2 1 1 22 20 27 16 12 32 4 9 22 3 4 2 3 12 25 2 13 23 2 6 10 1 1 1 2 1 1 4 1 6 5 3 1 2 1 1 2 11 2 2 3 1 1 1 3 65 33 33 3 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 37 15 15 15 54 54 54 54 50 54 54 54 54 54 54 54 54 54 54 54 54 54 21 21 21 21 21 21 21 21 21 21 21 54 54 54 54 54 34 34 34 31 34 25 25 25 25 25 25  61/65   20/33   3/33   1/3   35/37   30/37   14/37   22/37   18/37   26/37   17/37   23/37   14/37   14/37   15/37   19/37   11/37   10/37   12/37   36/37   36/37   36/37   30/37   2/15   1/15   1/15   22/54   20/54   27/54   16/54   12/50   32/54   4/54   9/54   22/54   3/54   4/54   2/54   3/54   12/54   25/54   2/54   13/54   23/54   2/21   6/21   10/21   1/21   1/21   1/21   2/21   1/21   1/21   4/21   1/21   6/54   5/54   3/54   1/54   2/54   1/34   1/34   2/34   11/31   2/34   2/25   3/25   1/25   1/25   1/25   3/25  94 61 9 33 95 81 38 59 49 70 46 62 38 38 41 51 30 27 32 97 97 97 81 13 7 7 41 37 50 30 24 59 7 17 41 6 7 4 6 22 46 4 24 43 10 29 48 5 5 5 10 5 5 19 5 11 9 6 2 4 3 3 6 35 6 8 12 4 4 4 12 0.78 0.0047 0.00208 0.00706 3.6E‐07 1.53E‐07 6.7E‐07 7.65E‐08 1.87E‐07 1.75E‐07 1.74E‐07 4.61E‐07 2.8E‐08 3.49E‐07 2.08E‐07 1.27E‐07 1.65E‐07 2.78E‐08 9.8E‐08 1.45E‐10 4.35E‐10 1.45E‐06 5.88E‐07 0.018 0.94 0.0014 0.0002 0.00023 0.00043 0.00025 0.00086 0.00033 0.00093 0.00093 0.00024 0.00089 0.00083 0.00051 0.00048 0.00037 0.00045 0.00089 0.00042 0.00079 0.00035 0.0004 0.00053 0.00055 0.00055 0.0005 0.00047 0.00058 0.00047 0.0004 0.00073 0.00059 0.00096 0.0044 0.00597 0.0287 0.016 0.000312 0.0027 0.000234 0.000372 0.0016 0.02 0.13 0.0021 0.0014 0.0025 8.19 0.099 0.046 0.00706 0.00149 0.000181 0.0000157 0.0000191 7.03E‐06 0.0000617 7.73E‐06 0.0000416 1.84E‐06 0.0000098 0.0000102 0.0000109 2.81E‐06 0.0000011 2.29E‐06 0.000025 0.0000519 0.0428 0.000642 0.032 0.94 0.0014 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.0012 0.012 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.0029 0.019 0.00055 0.00055 0.0005 0.0011 0.00058 0.00047 0.0047 0.00073 0.013 0.0023 0.099 0.00597 0.0503 0.016 0.000312 0.00281 0.000723 0.00136 1.5 1.5 0.13 0.0021 0.0014 0.12 1.5 0.0081 0.00712 0.0356 1.43E‐07 6.64E‐08 6.92E‐08 3.22E‐08 8.16E‐08 4.66E‐08 3.48E‐08 5.92E‐08 5.8E‐08 4.62E‐08 2.02E‐08 1.78E‐08 1.98E‐08 3.6E‐08 2.5E‐08 3.50E‐08 3.50E‐08 5.6E‐07 1.78E‐07 0.0107 2.14 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.0034 0.00284 0.00284 0.00284 0.00142 0.00284 0.00284 0.00284 0.00142 0.00142 0.00142 0.00142 0.0342 0.0342 0.0342 0.0342 0.0342 0.00914 0.00183 0.004 0.0034 0.0034 0.04 0.2 0.0064 0.04 0.04 0.2 2.8 0.106 0.106 0.0406 4.58E‐07 1.19E‐06 3.12E‐06 3.18E‐06 5.28E‐07 1.39E‐06 0.0000015 8.88E‐07 2.36E‐06 6.82E‐06 1.82E‐06 6.56E‐07 2.16E‐06 1.02E‐06 3.8E‐07 3.50E‐08 3.50E‐08 5.6E‐07 0.0000031 0.05 5.6 0.0044 0.8 0.044 0.044 0.044 0.044 0.042 0.044 0.8 0.042 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.8 0.034 0.034 0.004 0.0166 0.034 0.034 0.034 0.0166 0.0166 0.004 0.02 0.48 0.8 0.48 0.8 0.8 0.112 0.012 0.044 0.012 0.012 2 2 2 2 2 2 ELBS2023  ELBS3000  ELBS3003  ELBS2012  ELBS2012  ELBS3023  ELBS3023  ELBS2012  ELBS3012  ELBS3023  ELBS3012  ELBS2012  ELBS3023  ELBS2012  ELBS3003  ELBS3012  ELBS3012  ELBS2012  ELBS3003  ELBS2012  ELBS2012  ELBS2012  ELBS2009  ELBS2009  ELBS2000  ELBS2001  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  GMBS2012A  ELBS2022  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2007  ELBS2004  ELBS2007  ELBS2012  ELBS2012  ELBS2022  ELBS2009  ELBS2012  ELBS2012  ELBS2000  ELBS2000  ELBS2009  ELBS2022  ELBS2000  ELBS1012  ELBS1027  ELBS1012  ELBS1020  ELBS1013  ELBS1015  ELBS1019  ELBS1013  ELBS1019  ELBS1019  ELSV02  ELSV2016  ELSV1003  ELSV2006  ELSV2006  ELSV1003  4 0.5 0.5 6 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.5 1.2 6 1.5 1.5 1.5 1.5 1.5 1.5 1.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 6 0.5 0.5 0.5 1 1 1 1 6 6 6 6 1 6 6 5.5 5 5.5 5.5 5 =  =  =  J  =  =  =  =  =  =  =  =  J  =  =  =  J  =  =  =  =  =  =  =  J  J  =  =  =  =  =  =  =  =  =  J  J  =  =  =  =  J  =  =  J  J  J  J  J  J  J  J  J  J  J  J  J  J  J  =  J  J  J  J  =  =  =  =  J  J  =  3.46 0.0245 0.0057 NA  0.000223 0.0000276 0.00000194 0.00000263 0.00000115 0.00000808 0.00000109 0.00000599 0.000000307 0.00000129 0.000000982 0.00000144 0.000000312 0.000000128 0.000000277 0.00000394 0.00000708 0.00371 0.0000831 0.0164 NA  NA  0.0241 0.0153 0.0215 0.00596 0.0119 0.031 0.00316 0.00646 0.0499 0.00101 0.00145 0.000933 0.00113 0.00327 0.0465 0.00125 0.00126 0.0195 0.00108 0.00136 0.00273 NA  NA  NA  0.000785 NA  NA  0.00101 NA  0.00325 0.00141 0.00884 NA  0.0291 NA  NA  0.00276 0.000431 0.000866 0.0697 0.11 NA  NA  NA  0.0455 21  Standard  Deviation 1.41 0.0263 0.00832 NA  0.000369 0.000045 0.00000346 0.00000429 0.00000178 0.0000138 0.00000189 0.00000939 0.000000442 0.00000226 0.00000198 0.00000259 0.000000583 0.000000227 0.000000494 0.00000636 0.0000118 0.00758 0.000142 0.00829 NA  NA  0.162 0.0996 0.134 0.0309 0.0726 0.202 0.0128 0.0352 0.337 0.000136 0.00173 0.00261 0.000701 0.0176 0.31 0.00223 0.000453 0.122 0.000725 0.000838 0.00405 NA  NA  NA  0.000315 NA  NA  0.000901 NA  0.00441 0.00047 0.0131 NA  0.00305 NA  NA  0.000055 0.000167 0.000494 0.312 0.311 NA  NA  NA  0.0529 22 23   Recommend ed UCL  Recommended UCL Basis 3.76 0.0329 0.0105  NA  0.000835 0.0000604 0.00000293 0.00000379 0.00000166 0.0000182 0.00000163 0.00000869 0.000000441 0.00000195 0.00000155 0.00000218 0.000000483 0.000000197 0.00000042 0.00000856 0.0000157 0.00922 0.000187 0.0257 3.03 0.00199 0.122 0.0759 0.138 0.0249 0.0586 0.205 0.00655 0.0288 0.254 0.00117 0.00206 0.00681 0.00196 0.0143 0.234 0.00345 0.00148 0.054 0.00578 0.00197 0.00436 0.00276 0.00563 0.00563 0.00133 0.00341 0.00276 0.00155 0.00331 0.00656 0.00181 0.0141 0.0791 0.0302 0.0228 0.0039 0.00285 0.000521 0.0017 1.01 0.255 0.534 0.534 0.534 0.109 95% KM (t) UCL 95% KM (Percentile Bootstrap) 95% KM (t) UCL Fewer Than Five Samples 99% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% Chebyshev UCL* 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 95% Chebyshev UCL* 95% Chebyshev UCL* 95% Chebyshev UCL* 95% KM (t) UCL 24 RME EPC 3.76 0.0329 0.0105 0.00706 0.000835 0.0000604 0.00000293 0.00000379 0.00000166 0.0000182 0.00000163 0.00000869 0.000000441 0.00000195 0.00000155 0.00000218 0.000000483 0.000000197 0.00000042 0.00000856 0.0000157 0.00922 0.000187 0.0257 0.94 0.0014 0.122 0.0759 0.138 0.0249 0.0586 0.205 0.00655 0.0288 0.254 0.00117 0.00206 0.00681 0.00196 0.0143 0.234 0.00345 0.00148 0.054 0.0018 0.00197 0.00436 0.00055 0.00055 0.0005 0.0011 0.00058 0.00047 0.00155 0.00073 0.00656 0.00181 0.0141 0.00597 0.0302 0.016 0.000312 0.00281 0.000521 0.00136 1.01 0.255 0.13 0.0021 0.0014 0.109 25 RME EPC Basis 95% KM (t) UCL 95% KM (Percentile Bootstrap) 95% KM (t) UCL Maximum Result 99% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL Maximum Result Maximum Result 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 97.5% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (t) UCL 99% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (Chebyshev) UCL 95% KM (t) UCL 95% KM (BCA) UCL Maximum Result 95% KM (t) UCL 95% KM (t) UCL Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result Maximum Result 95% KM (t) UCL Maximum Result 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL Maximum Result 95% KM (t) UCL Maximum Result Maximum Result Maximum Result 95% KM (t) UCL Maximum Result 99% KM (Chebyshev) UCL 95% KM (t) UCL Maximum Result Maximum Result Maximum Result 95% KM (t) UCL PAGE 4 OF 5 ATTACHMENT 1, TABLE 4 Summary Statistics for Detected Analytes RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California 14  Matrix  Depth  Interval Type Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft O O O O O  EcoRAClass VOC VOC VOC VOC VOC Preferred Analyte Name Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Xylenes, Total 15 16 17 18 19 20 Qualifier of  Depth of  Location of    Minimum  Maximum  Maximum  Maximum  Maximum  Detected  Detected  Detected  SQL for   Minimum  Maximum  SQL for   Number   Number  Concentratio Concentratio Concentratio  Arithmetic  Non‐ Non‐ of   Frequency   Percent  Detected  Detected  of  n Mean Value n n detects detects Value Value  Units Detects Analyses of Detects Detects µg/L µg/L µg/L µg/L µg/L 1 4 3 2 5 25 25 25 25 25  1/25   4/25   3/25   2/25   5/25  4 16 12 8 20 0.0095 0.00089 5.7 0.02 0.0085 0.0095 0.95 120 0.022 0.54 0.04 0.046 0.0108 0.2 0.2 2 2 2 2 4 ELSV2006  ELSV1003  ELSV02  ELSV3000  ELSV1003  5.5 5 6 5.5 5 =  =  =  =  =  NA  0.098 5.41 0.021 0.0751 21  Standard  Deviation NA  0.202 23.5 0.001 0.127 22 23   Recommend ed UCL  Recommended UCL Basis 0.587 0.203 15.3 0.0227 0.133 95% Chebyshev UCL* 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 95% KM (t) UCL 24 25 RME EPC RME EPC Basis 0.0095 0.203 15.3 0.022 0.133 Maximum Result 95% KM (t) UCL 95% KM (t) UCL Maximum Result 95% KM (t) UCL Notes: *  ProUCL Version 5 does not offer a calculated UCL when there are too few unique detected results (one or sometimes more than one). In these cases, the 95% Chebyshev UCL using a proxy value of 1/2 the detection limit for NDs was selected as the EPC.   µg/L = micrograms per liter BHC = benzene hexachloride CPEC = chemical of potential ecological concern ERA = ecological risk assessment ESL = ecological screening level  ft = feet  MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight NA = not available NSD = no significant difference PAH = polcyclic aromatic hydrocarbon RBSL = risk‐based screening level SQL = sample quantitation limit SVOC = semivolatile organic compound TEQ = toxicity equivalent  UCL = upper confidence limit on the mean VOC = volatile organic compound EN0411151012BAO  PAGE 5 OF 5 ATTACHMENT 1, TABLE 5 Central Tendency Background Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Matrix Depth Measured Data Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft Soil 0‐2 ft EN0411151012BAO  Type EcoRAClass I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I O O O O O O O O O O O O O O Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Preferred Analyte Name Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Iron Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Phosphorus Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD Units mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg Central Tendency Comparisons Probability that the  Statistical  Observed  Decision  Differences Would  with 0.05  Mean of   Mean of   Median  Comparison  Occur Purely by  Signficance  Site  Bkgd  of Site  Test Used Chance Level Detects Detects Detects Gehan  WRS  Gehan  WRS  WRS  WRS  Gehan  WRS  WRS  WRS  WRS  Gehan  Gehan  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  WRS  Gehan  WRS  WRS  WRS  WRS  Gehan  WRS  WRS  Gehan  WRS  Gehan  Gehan  0.050 1.000 0.618 1.000 0.991 0.997 1.000 0.500 1.000 1.000 1.000 0.764 0.140 0.999 1.000 1.000 0.999 0.500 0.500 1.000 1.000 0.999 0.500 0.000 0.820 0.500 0.790 1.000 1.000 0.985 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.188 0.000 0.000 0.000 0.000 0.048 0.000 Site > Bkgd 0.014 0.000538 0.014 nsd 16800 21200 15900 nsd 0.763 0.246 0.285 nsd 13.4 10.3 6.17 nsd 113 127 111 nsd 0.75 0.883 0.769 nsd 4.47 9.47 4.39 nsd 0.227 0.257 0.21 nsd 20 38.2 20.4 nsd 6.68 12.8 6.23 nsd 12.2 18.2 11 nsd 1.44 2.41 1.5 nsd 1.13 0.621 0.865 nsd 20000 31800 19700 nsd 8.45 15.2 7.93 nsd 19.2 32.7 19 nsd 375 426 347 nsd 0.0112 0.0155 0.00905 nsd 0.511 0.896 0.491 nsd 14.2 26.3 13.8 nsd 1.42 4.16 1.03 nsd 212 541 207 nsd 0.199 0.292 0.17 Site > Bkgd 0.223 0.0498 0.0568 nsd 25 33.3 25.1 nsd 0.269 0.369 0.256 nsd 933 1090 851 nsd 41.3 70.7 41.8 nsd 51.8 90.1 47.9 nsd 3.46 4.94 3.57 Site > Bkgd 4.45E‐05 3.00E‐07 2.48E‐05 Site > Bkgd 0.000336 1.20E‐06 0.000219 Site > Bkgd 5.60E‐06 0 4.00E‐06 Site > Bkgd 2.50E‐06 0 2.10E‐06 Site > Bkgd 5.00E‐06 0 3.10E‐06 Site > Bkgd 2.50E‐06 0 1.40E‐06 Site > Bkgd 1.34E‐05 3.00E‐07 8.10E‐06 nsd 7.00E‐07 3.00E‐07 5.00E‐07 Site > Bkgd 1.04E‐05 3.00E‐07 6.60E‐06 Site > Bkgd 2.40E‐06 0 1.50E‐06 Site > Bkgd 3.70E‐06 0 3.80E‐06 Site > Bkgd 3.10E‐06 1.00E‐07 2.30E‐06 Site > Bkgd 1.00E‐06 1.00E‐07 9.00E‐07 Site > Bkgd 4.00E‐07 0 4.00E‐07 Descriptive Site/Bkgd Statistics  Median   Number   Number   Number   Number   Percent  of Bkgd  of Site  of Site  of Bkgd  of Bkgd  Detects  Detects Detects Samples Detects Samples Site 0.00047 19900 0.224 9.15 125 0.831 8.2 0.242 38 11.3 15.6 1.67 0.539 30600 13.4 29.8 403 0.0129 0.847 22.4 2.6 530 0.268 0.0425 27.9 0.361 1030 69 86.6 4.73 3.00E‐07 1.10E‐06 0 0 0 0 2.00E‐07 2.00E‐07 2.00E‐07 0 0 0 0 0 2 40 20 49 42 38 21 41 40 40 41 12 10 4 38 37 23 16 36 40 6 4 27 35 4 35 4 40 40 36 22 23 12 15 18 15 21 13 20 14 11 16 10 8 10 40 42 52 42 40 38 43 40 40 41 21 19 4 40 37 23 25 40 40 10 4 40 43 4 40 4 40 40 37 23 23 23 23 23 23 23 23 23 23 23 23 23 23 73 267 260 267 268 267 216 267 268 268 268 158 201 267 268 268 267 212 267 268 249 268 266 266 268 268 268 268 268 261 146 147 126 142 126 145 146 142 146 144 132 145 143 17 268 267 267 267 268 267 268 268 268 268 268 267 268 267 268 268 267 260 267 268 266 268 266 268 268 268 268 268 268 266 147 147 147 147 146 147 148 147 148 147 145 147 147 147 20 100 48 94 100 95 55 95 100 100 100 57 53 100 95 100 100 64 90 100 60 100 68 81 100 88 100 100 100 97 96 100 52 65 78 65 91 57 87 61 48 70 43 35 Individual Criteria  Comparisons Number of  Samples   Percent  Exceeding  Detects  Background 95‐ Bkgd 95UTL 27 100 97 100 100 100 81 100 100 100 100 59 75 100 100 100 100 82 100 100 94 100 100 99 100 100 100 100 100 98 99 100 86 97 86 99 99 97 99 98 91 99 97 12 2 0 5 5 0 0 0 4 0 0 0 0 2 0 0 0 1 1 0 0 0 0 0 9 0 0 0 0 0 0 18 19 12 15 18 15 15 3 15 14 11 14 9 8 PAGE 1 OF 6 ATTACHMENT 1, TABLE 5 Central Tendency Background Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Depth 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O I I I I I EcoRAClass Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC Energetics Inorganics Inorganics Inorganics Inorganics Preferred Analyte Name 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4‐Dichlorophenoxybutyric acid MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Perchlorate Aluminum Antimony Arsenic Barium Units mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg Central Tendency Comparisons Probability that the  Statistical  Observed  Decision  Differences Would  with 0.05  Comparison  Occur Purely by  Signficance  Test Used Chance Level Gehan  0.160 nsd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.001 Site > Bkgd Gehan  0.121 nsd Gehan  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.004 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.222 nsd WRS  0.001 Site > Bkgd Gehan  0.002 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.001 Site > Bkgd Gehan  0.009 Site > Bkgd Gehan  0.016 Site > Bkgd ‐‐ ‐‐ ‐‐ Gehan  0.006 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.005 Site > Bkgd Gehan  0.352 nsd Gehan  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.070 nsd Gehan  0.391 nsd WRS  0.074 nsd Gehan  0.170 nsd Gehan  0.203 nsd Gehan  0.191 nsd Gehan  0.210 nsd Gehan  0.120 nsd Gehan  0.267 nsd Gehan  0.005 Site > Bkgd Gehan  0.920 nsd Gehan  0.934 nsd Gehan  0.507 nsd Gehan  0.548 nsd Gehan  0.023 Site > Bkgd Gehan  0.050 Site > Bkgd WRS  0.999 nsd Gehan  0.758 nsd WRS  1.000 nsd WRS  0.986 nsd Descriptive Site/Bkgd Statistics Mean of  Site  Detects 7.00E‐07 5.90E‐06 1.07E‐05 0.000133 0.00544 0.025 0.94 0.0947 0.0645 0.0639 0.0218 0.0887 0.0838 0.0268 0.0386 0.199 0.00107 0.00135 ‐‐ 0.00113 0.0196 0.171 0.00795 0.00133 0.0687 0.00108 0.00143 0.00478 0.00073 0.00055 0.00055 0.0005 0.000785 0.00047 0.00179 0.0287 0.00441 0.00597 0.00157 0.0377 0.014 17000 0.763 13.3 115  Mean of  Bkgd  Detects 1.00E‐07 4.00E‐07 2.00E‐07 6.00E‐07 8.30E‐06 0.00696 0.425 0.00128 0.00126 0.00149 0.00107 0.00246 0.00112 0.00111 0.00083 0.00128 0.00093 0.00108 ‐‐ 0.00123 0.000773 0.00135 0.0019 0.00135 0.00116 0.000161 0.0013 0.00162 0.00013 7.71E‐05 0.000171 0.000156 0.000212 8.18E‐05 0.000175 0.0192 0.0246 0.0152 0.00856 0.00646 0.000538 21200 0.246 10.3 127  Median  of Site  Detects 6.00E‐07 3.20E‐06 6.40E‐06 6.79E‐05 0.00288 0.025 0.94 0.002 0.00265 0.0028 0.00168 0.0029 0.0024 0.00505 0.0019 0.004 0.00107 0.00135 ‐‐ 0.0008 0.00062 0.0029 0.00795 0.00115 0.00195 0.00108 0.00135 0.0034 0.00073 0.00055 0.00055 0.0005 0.000785 0.00047 0.00104 0.0287 0.00195 0.00597 0.0013 0.0096 0.014 15900 0.285 6.3 111  Median   Number   Number   Number   Number   Percent  of Bkgd  of Site  of Site  of Bkgd  of Bkgd  Detects  Detects Detects Samples Detects Samples Site 1.00E‐07 12 23 145 147 52 3.00E‐07 23 23 147 147 100 2.00E‐07 23 23 147 147 100 5.00E‐07 22 23 146 147 96 7.40E‐06 23 23 143 143 100 0.0034 2 9 13 148 22 0.45 1 9 18 148 11 0.001 13 31 13 144 42 0.000895 12 31 28 147 39 0.0011 17 31 107 148 55 0.0009 12 31 19 147 39 0.0019 6 28 46 146 21 0.00089 19 31 135 145 61 0.000895 4 31 8 148 13 0.000825 7 31 8 145 23 0.001 13 31 98 147 42 0.00088 2 31 3 148 6 0.00108 2 31 4 148 6 ‐‐ 2 31 ‐‐ ‐‐ 6 0.00071 3 31 5 148 10 0.000728 7 31 6 148 23 0.0012 14 31 112 147 45 0.0021 2 31 17 148 6 0.001 10 31 27 147 32 0.00088 14 31 61 148 45 0.000138 2 13 30 146 15 0.00074 6 13 138 147 46 0.00078 9 13 147 148 69 0.000105 1 13 16 147 8 0.000069 1 13 23 147 8 0.000135 1 13 20 148 8 0.00013 1 13 24 147 8 0.000145 2 13 69 145 15 0.000072 1 13 50 145 8 0.00015 4 13 66 144 31 0.019 1 31 53 141 3 0.017 4 31 51 148 13 0.0152 1 31 1 148 3 0.0085 3 31 5 145 10 0.0064 3 31 6 141 10 0.00047 2 10 73 268 20 19900 42 42 267 267 100 0.224 20 44 260 267 45 9.15 51 55 267 267 93 125 44 44 268 268 100 Individual Criteria  Comparisons Number of  Samples   Percent  Exceeding  Detects  Background 95‐ Bkgd 95UTL 99 10 100 14 100 15 99 22 100 22 9 1 12 1 9 8 19 6 72 8 13 7 32 2 93 8 5 3 6 7 67 8 2 0 3 0 ‐‐ 1 3 1 4 3 76 8 11 1 18 2 41 7 21 2 94 0 99 2 11 1 16 1 14 1 16 1 48 2 34 1 46 4 38 1 34 0 1 0 3 0 4 2 27 2 100 0 97 5 100 5 100 0 PAGE 2 OF 6 ATTACHMENT 1, TABLE 5 Central Tendency Background Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Depth 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  Type I I I I I I I I I I I I I I I I I I I I I I I I I O O O O O O O O O O O O O O O O O O O O EcoRAClass Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Preferred Analyte Name Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Hexavalent Chromium Iron Lead Lithium Manganese Mercury Molybdenum Nickel Nitrate‐N Selenium Silver Strontium Thallium Titanium Vanadium Zinc Zirconium Phosphorus 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzofuran 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4‐Dichlorophenoxybutyric acid Units mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg Central Tendency Comparisons Probability that the  Statistical  Observed  Decision  Differences Would  with 0.05  Comparison  Occur Purely by  Signficance  Test Used Chance Level WRS  0.993 nsd Gehan  1.000 nsd WRS  0.500 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  1.000 nsd Gehan  0.764 nsd Gehan  0.137 nsd WRS  0.999 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  0.997 nsd WRS  0.500 nsd WRS  0.500 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  0.500 nsd WRS  0.000 Site > Bkgd WRS  0.820 nsd WRS  0.500 nsd WRS  0.790 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  0.976 nsd WRS  0.999 nsd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.260 nsd WRS  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.097 nsd Gehan  0.000 Site > Bkgd Gehan  0.238 nsd WRS  0.001 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.001 Site > Bkgd Descriptive Site/Bkgd Statistics Mean of   Mean of   Median  Site  Bkgd  of Site  Detects Detects Detects 0.755 0.883 0.769 4.47 9.47 4.39 0.224 0.257 0.199 20.8 38.2 22.1 6.79 12.8 6.45 12.5 18.2 11.4 1.44 2.41 1.5 1.08 0.621 0.85 20000 31800 19700 8.52 15.2 7.93 20.4 32.7 19.3 379 426 360 0.0112 0.0155 0.00905 0.503 0.896 0.48 15 26.3 14 1.42 4.16 1.03 0.2 0.292 0.17 0.215 0.0498 0.0568 25 33.3 25.1 0.275 0.369 0.271 933 1090 851 42.2 70.7 42 53.2 90.1 48.5 3.6 4.94 3.62 212 541 207 4.26E‐05 3.00E‐07 2.32E‐05 0.000323 1.20E‐06 0.000172 5.60E‐06 0 4.00E‐06 2.50E‐06 0 2.10E‐06 4.70E‐06 0 2.80E‐06 2.50E‐06 0 1.40E‐06 1.34E‐05 3.00E‐07 8.10E‐06 7.00E‐07 3.00E‐07 5.00E‐07 1.04E‐05 3.00E‐07 6.60E‐06 2.40E‐06 0 1.50E‐06 3.70E‐06 0 3.80E‐06 3.10E‐06 1.00E‐07 2.30E‐06 1.00E‐06 1.00E‐07 9.00E‐07 4.00E‐07 0 4.00E‐07 7.00E‐07 1.00E‐07 6.00E‐07 5.70E‐06 4.00E‐07 2.70E‐06 1.02E‐05 2.00E‐07 4.80E‐06 0.000127 6.00E‐07 6.78E‐05 0.00522 8.30E‐06 0.00284 0.025 0.00696 0.025  Median   Number   Number   Number   Number   Percent  of Bkgd  of Site  of Site  of Bkgd  of Bkgd  Detects  Detects Detects Samples Detects Samples Site 0.831 40 42 267 267 95 8.2 21 40 216 268 53 0.242 43 45 267 268 96 38 43 43 268 268 100 11.3 42 42 268 268 100 15.6 43 43 268 268 100 1.67 12 21 158 267 57 0.539 11 20 201 268 55 30600 4 4 267 267 100 13.4 40 42 268 268 95 29.8 39 39 268 268 100 403 25 25 267 267 100 0.0129 16 25 212 260 64 0.847 38 42 267 267 90 22.4 42 42 268 268 100 2.6 6 10 249 266 60 0.268 28 42 266 266 67 0.0425 37 45 266 268 82 27.9 4 4 268 268 100 0.361 37 42 268 268 88 1030 4 4 268 268 100 69 42 42 268 268 100 86.6 42 42 268 268 100 4.73 38 39 261 266 97 530 4 4 268 268 100 3.00E‐07 23 24 146 147 96 1.10E‐06 24 24 147 147 100 0 12 24 126 147 50 0 15 24 142 147 63 0 19 24 126 146 79 0 15 24 145 147 63 2.00E‐07 21 24 146 148 88 2.00E‐07 13 24 142 147 54 2.00E‐07 20 24 146 148 83 0 14 24 144 147 58 0 11 24 132 145 46 0 16 24 145 147 67 0 10 24 143 147 42 0 8 24 17 147 33 1.00E‐07 12 24 145 147 50 3.00E‐07 24 24 147 147 100 2.00E‐07 24 24 147 147 100 5.00E‐07 23 24 146 147 96 7.40E‐06 24 24 143 143 100 0.0034 2 9 13 148 22 Individual Criteria  Comparisons Number of  Samples   Percent  Exceeding  Detects  Background 95‐ Bkgd 95UTL 100 0 81 0 100 4 100 0 100 0 100 0 59 0 75 2 100 0 100 0 100 0 100 1 82 1 100 0 100 0 94 0 100 0 99 10 100 0 100 0 100 0 100 0 100 0 98 0 100 0 99 19 100 20 86 12 97 15 86 19 99 15 99 15 97 3 99 15 98 14 91 11 99 14 97 9 12 8 99 10 100 14 100 15 99 23 100 23 9 1 PAGE 3 OF 6 ATTACHMENT 1, TABLE 5 Central Tendency Background Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Depth 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O I I I I I I I I I I I I EcoRAClass Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics Preferred Analyte Name MCPA Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor epoxide Mirex bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Perchlorate Aluminum Antimony Arsenic Barium Beryllium Boron Cadmium Chromium Cobalt Copper Fluoride Units mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg Central Tendency Comparisons Descriptive Site/Bkgd Statistics Probability that the  Statistical  Observed  Decision  Differences Would  with 0.05  Mean of   Mean of   Median   Median   Number   Number   Number   Number   Percent  Comparison  Occur Purely by  Signficance  Site  Bkgd  of Site  of Bkgd  of Site  of Site  of Bkgd  of Bkgd  Detects  Test Used Chance Level Detects Detects Detects Detects Detects Samples Detects Samples Site Gehan  0.121 nsd 0.94 0.425 0.94 0.45 1 9 18 148 11 Gehan  0.000 Site > Bkgd 0.0947 0.00128 0.002 0.001 13 32 13 144 41 Gehan  0.000 Site > Bkgd 0.0645 0.00126 0.00265 0.000895 12 32 28 147 38 Gehan  0.005 Site > Bkgd 0.0639 0.00149 0.0028 0.0011 17 32 107 148 53 Gehan  0.000 Site > Bkgd 0.0218 0.00107 0.00168 0.0009 12 32 19 147 38 Gehan  0.245 nsd 0.0887 0.00246 0.0029 0.0019 6 29 46 146 21 WRS  0.002 Site > Bkgd 0.0797 0.00112 0.00205 0.00089 20 32 135 145 63 Gehan  0.003 Site > Bkgd 0.0268 0.00111 0.00505 0.000895 4 32 8 148 13 Gehan  0.000 Site > Bkgd 0.0386 0.00083 0.0019 0.000825 7 32 8 145 22 Gehan  0.001 Site > Bkgd 0.199 0.00128 0.004 0.001 13 32 98 147 41 Gehan  0.010 Site > Bkgd 0.00107 0.00093 0.00107 0.00088 2 32 3 148 6 Gehan  0.017 Site > Bkgd 0.00135 0.00108 0.00135 0.00108 2 32 4 148 6 Gehan  0.006 Site > Bkgd 0.00113 0.00123 0.0008 0.00071 3 32 5 148 9 Gehan  0.000 Site > Bkgd 0.0196 0.000773 0.00062 0.000728 7 32 6 148 22 Gehan  0.007 Site > Bkgd 0.159 0.00135 0.0027 0.0012 15 32 112 147 47 Gehan  0.368 nsd 0.00795 0.0019 0.00795 0.0021 2 32 17 148 6 Gehan  0.000 Site > Bkgd 0.00133 0.00135 0.00115 0.001 10 32 27 147 31 Gehan  0.000 Site > Bkgd 0.0687 0.00116 0.00195 0.00088 14 32 61 148 44 Gehan  0.070 nsd 0.00108 0.000161 0.00108 0.000138 2 13 30 146 15 Gehan  0.391 nsd 0.00143 0.0013 0.00135 0.00074 6 13 138 147 46 WRS  0.074 nsd 0.00478 0.00162 0.0034 0.00078 9 13 147 148 69 Gehan  0.170 nsd 0.00073 0.00013 0.00073 0.000105 1 13 16 147 8 Gehan  0.203 nsd 0.00055 7.71E‐05 0.00055 0.000069 1 13 23 147 8 Gehan  0.191 nsd 0.00055 0.000171 0.00055 0.000135 1 13 20 148 8 Gehan  0.210 nsd 0.0005 0.000156 0.0005 0.00013 1 13 24 147 8 Gehan  0.120 nsd 0.000785 0.000212 0.000785 0.000145 2 13 69 145 15 Gehan  0.267 nsd 0.00047 8.18E‐05 0.00047 0.000072 1 13 50 145 8 Gehan  0.005 Site > Bkgd 0.00179 0.000175 0.00104 0.00015 4 13 66 144 31 Gehan  0.926 nsd 0.0287 0.0192 0.0287 0.019 1 32 53 141 3 Gehan  0.938 nsd 0.00441 0.0246 0.00195 0.017 4 32 51 148 13 Gehan  0.507 nsd 0.00597 0.0152 0.00597 0.0152 1 32 1 148 3 Gehan  0.548 nsd 0.00157 0.00856 0.0013 0.0085 3 32 5 145 9 Gehan  0.024 Site > Bkgd 0.0377 0.00646 0.0096 0.0064 3 32 6 141 9 Gehan  0.007 Site > Bkgd 0.019 0.000538 0.0146 0.00047 4 18 73 268 22 WRS  1.000 nsd 17400 21200 17100 19900 68 68 267 267 100 Gehan  0.982 nsd 0.61 0.246 0.277 0.224 29 71 260 267 41 WRS  1.000 nsd 12.9 10.3 7 9.15 83 87 267 267 95 WRS  1.000 nsd 110 127 109 125 72 72 268 268 100 WRS  0.996 nsd 0.785 0.883 0.772 0.831 66 68 267 267 97 Gehan  1.000 nsd 4.81 9.47 4.66 8.2 34 66 216 268 52 WRS  0.500 nsd 0.184 0.257 0.146 0.242 71 73 267 268 97 WRS  1.000 nsd 22.3 38.2 22.7 38 69 69 268 268 100 WRS  1.000 nsd 6.68 12.8 6.1 11.3 68 68 268 268 100 WRS  1.000 nsd 12 18.2 11 15.6 69 69 268 268 100 Gehan  0.322 nsd 2.39 2.41 1.71 1.67 22 35 158 267 63 Individual Criteria  Comparisons Number of  Samples   Percent  Exceeding  Detects  Background 95‐ Bkgd 95UTL 12 1 9 8 19 6 72 8 13 7 32 2 93 8 5 3 6 7 67 8 2 0 3 0 3 1 4 3 76 8 11 1 18 2 41 7 21 2 94 0 99 2 11 1 16 1 14 1 16 1 48 2 34 1 46 4 38 1 34 0 1 0 3 0 4 2 27 4 100 0 97 6 100 8 100 1 100 1 81 0 100 4 100 0 100 0 100 0 59 2 PAGE 4 OF 6 ATTACHMENT 1, TABLE 5 Central Tendency Background Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Depth 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  Type I I I I I I I I I IG I I I I I I I I I O O O O O O O O O O O O O O O O O O O O O O O O O O EcoRAClass Preferred Analyte Name Inorganics Hexavalent Chromium Inorganics Iron Inorganics Lead Inorganics Lithium Inorganics Manganese Inorganics Mercury Inorganics Molybdenum Inorganics Nickel Inorganics Nitrate‐N General ChemistrPhosphorus Inorganics Selenium Inorganics Silver Inorganics Strontium Inorganics Thallium Inorganics Tin Inorganics Titanium Inorganics Vanadium Inorganics Zinc Inorganics Zirconium Dioxin_Furans 1,2,3,4,6,7,8‐Heptachlorodibenzofuran Dioxin_Furans 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin Dioxin_Furans 1,2,3,4,7,8,9‐Heptachlorodibenzofuran Dioxin_Furans 1,2,3,4,7,8‐Hexachlorodibenzofuran Dioxin_Furans 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin Dioxin_Furans 1,2,3,6,7,8‐Hexachlorodibenzofuran Dioxin_Furans 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin Dioxin_Furans 1,2,3,7,8,9‐Hexachlorodibenzofuran Dioxin_Furans 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin Dioxin_Furans 1,2,3,7,8‐Pentachlorodibenzofuran Dioxin_Furans 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin Dioxin_Furans 2,3,4,6,7,8‐Hexachlorodibenzofuran Dioxin_Furans 2,3,4,7,8‐Pentachlorodibenzofuran Dioxin_Furans 2,3,7,8‐TCDD Dioxin_Furans 2,3,7,8‐Tetrachlorodibenzofuran Dioxin_Furans DioxinFuran_TEQ_Bird Dioxin_Furans DioxinFuran_TEQ_Mammal Dioxin_Furans Octachlorodibenzofuran Dioxin_Furans Octachlorodibenzo‐p‐dioxin Herbicides 2,4‐Dichlorophenoxybutyric acid Herbicides MCPA Herbicides Silvex PAH‐HighMW Benzo(a)anthracene PAH‐HighMW Benzo(a)pyrene PAH‐HighMW Benzo(b)fluoranthene PAH‐HighMW Benzo(ghi)perylene Units mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg Central Tendency Comparisons Probability that the  Statistical  Observed  Decision  Differences Would  with 0.05  Comparison  Occur Purely by  Signficance  Test Used Chance Level Gehan  0.453 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  0.500 nsd WRS  0.500 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  1.000 nsd Gehan  1.000 nsd WRS  0.003 Site > Bkgd WRS  0.740 nsd WRS  0.500 nsd Gehan  0.290 nsd WRS  0.860 nsd WRS  1.000 nsd WRS  1.000 nsd WRS  0.996 nsd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.001 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.042 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.976 nsd WRS  0.000 Site > Bkgd Gehan  0.021 Site > Bkgd Gehan  0.010 Site > Bkgd Gehan  0.030 Site > Bkgd Gehan  0.870 nsd Gehan  0.000 Site > Bkgd Gehan  0.993 nsd WRS  0.250 nsd WRS  0.024 Site > Bkgd WRS  0.000 Site > Bkgd WRS  0.000 Site > Bkgd Gehan  0.013 Site > Bkgd Gehan  0.174 nsd Gehan  0.252 nsd Gehan  0.000 Site > Bkgd Gehan  0.000 Site > Bkgd Gehan  0.003 Site > Bkgd Gehan  0.000 Site > Bkgd Descriptive Site/Bkgd Statistics Mean of   Mean of   Median   Median   Number   Number   Number   Number   Percent  Site  Bkgd  of Site  of Bkgd  of Site  of Site  of Bkgd  of Bkgd  Detects  Detects Detects Detects Detects Detects Samples Detects Samples Site 1.01 0.621 0.845 0.539 14 27 201 268 52 19800 31800 19700 30600 6 6 267 267 100 7.95 15.2 7.48 13.4 66 68 268 268 97 24.8 32.7 23 29.8 65 65 268 268 100 343 426 314 403 42 42 267 267 100 0.011 0.0155 0.00929 0.0129 26 39 212 260 67 0.413 0.896 0.382 0.847 60 68 267 267 88 16.3 26.3 15.1 22.4 68 68 268 268 100 1.43 4.16 1.1 2.6 10 15 249 266 67 205 541 207 530 6 6 268 268 100 0.223 0.292 0.182 0.268 34 68 266 266 50 0.175 0.0498 0.0638 0.0425 60 71 266 268 85 27.4 33.3 25.1 27.9 6 6 268 268 100 0.27 0.369 0.255 0.361 62 68 268 268 91 0.384 3.15 0.384 3.13 1 6 28 268 17 920 1090 896 1030 6 6 268 268 100 42.1 70.7 42 69 68 68 268 268 100 52.5 90.1 49.3 86.6 68 68 268 268 100 3.6 4.94 3.65 4.73 61 65 261 266 94 0.000034 3.00E‐07 1.12E‐05 3.00E‐07 30 37 146 147 81 0.000236 1.20E‐06 4.41E‐05 1.10E‐06 35 37 147 147 95 4.90E‐06 0 3.50E‐06 0 14 37 126 147 38 2.20E‐06 0 1.20E‐06 0 18 37 142 147 49 4.30E‐06 0 2.80E‐06 0 22 37 126 146 59 2.20E‐06 0 1.40E‐06 0 17 37 145 147 46 1.15E‐05 3.00E‐07 5.70E‐06 2.00E‐07 26 37 146 148 70 6.00E‐07 3.00E‐07 5.00E‐07 2.00E‐07 14 37 142 147 38 9.50E‐06 3.00E‐07 6.30E‐06 2.00E‐07 23 37 146 148 62 2.30E‐06 0 1.50E‐06 0 15 37 144 147 41 3.20E‐06 0 2.30E‐06 0 14 37 132 145 38 2.70E‐06 1.00E‐07 1.50E‐06 0 19 37 145 147 51 9.00E‐07 1.00E‐07 9.00E‐07 0 11 37 143 147 30 3.00E‐07 0 3.00E‐07 0 10 37 17 147 27 7.00E‐07 1.00E‐07 6.00E‐07 1.00E‐07 12 37 145 147 32 4.00E‐06 4.00E‐07 6.00E‐07 3.00E‐07 36 37 147 147 97 7.20E‐06 2.00E‐07 8.00E‐07 2.00E‐07 36 37 147 147 97 0.000102 6.00E‐07 3.94E‐05 5.00E‐07 30 37 146 147 81 0.00381 8.30E‐06 0.000596 7.40E‐06 36 37 143 143 97 0.025 0.00696 0.025 0.0034 2 15 13 148 13 0.94 0.425 0.94 0.45 1 15 18 148 7 0.0014 0.000248 0.0014 0.00021 1 15 37 147 7 0.0568 0.00128 0.0017 0.001 22 54 13 144 41 0.0392 0.00126 0.00126 0.000895 20 54 28 147 37 0.0408 0.00149 0.002 0.0011 27 54 107 148 50 0.0166 0.00107 0.0012 0.0009 16 54 19 147 30 Individual Criteria  Comparisons Number of  Samples   Percent  Exceeding  Detects  Background 95‐ Bkgd 95UTL 75 3 100 0 100 0 100 0 100 2 82 1 100 0 100 0 94 0 100 0 100 0 99 20 100 0 100 0 10 0 100 0 100 0 100 0 98 0 99 23 100 27 86 14 97 18 86 22 99 17 99 18 97 3 99 18 98 15 91 14 99 17 97 9 12 10 99 10 100 17 100 18 99 29 100 30 9 1 12 1 25 1 9 12 19 7 72 9 13 8 PAGE 5 OF 6 ATTACHMENT 1, TABLE 5 Central Tendency Background Comparisons for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Depth 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft Type O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O EcoRAClass PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC Preferred Analyte Name Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene 1‐Methyl naphthalene 2‐Methylnaphthalene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDE 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex bis(2‐Ethylhexyl) phthalate Butyl benzyl phthalate Diethyl phthalate Di‐n‐butyl phthalate Di‐n‐octyl phthalate Units mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg mg/Kg Central Tendency Comparisons Descriptive Site/Bkgd Statistics Probability that the  Statistical  Observed  Decision  Differences Would  with 0.05  Mean of   Mean of   Median   Median   Number   Number   Number   Number   Percent  Comparison  Occur Purely by  Signficance  Site  Bkgd  of Site  of Bkgd  of Site  of Site  of Bkgd  of Bkgd  Detects  Test Used Chance Level Detects Detects Detects Detects Detects Samples Detects Samples Site Gehan  0.183 nsd 0.0449 0.00246 0.0012 0.0019 12 50 46 146 24 Gehan  0.000 Site > Bkgd 0.0509 0.00112 0.00225 0.00089 32 54 135 145 59 Gehan  0.011 Site > Bkgd 0.0268 0.00111 0.00505 0.000895 4 54 8 148 7 Gehan  0.000 Site > Bkgd 0.0303 0.00083 0.0014 0.000825 9 54 8 145 17 Gehan  0.000 Site > Bkgd 0.119 0.00128 0.004 0.001 22 54 98 147 41 Gehan  0.003 Site > Bkgd 0.00101 0.00093 0.00094 0.00088 3 54 3 148 6 Gehan  0.001 Site > Bkgd 0.00388 0.00108 0.00135 0.00108 4 54 4 148 7 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 54 ‐‐ ‐‐ 4 Gehan  0.022 Site > Bkgd 0.00113 0.00123 0.0008 0.00071 3 54 5 148 6 Gehan  0.000 Site > Bkgd 0.0118 0.000773 0.000755 0.000728 12 54 6 148 22 Gehan  0.000 Site > Bkgd 0.0976 0.00135 0.0027 0.0012 25 54 112 147 46 Gehan  0.563 nsd 0.00795 0.0019 0.00795 0.0021 2 54 17 148 4 Gehan  0.000 Site > Bkgd 0.00126 0.00135 0.0011 0.001 13 54 27 147 24 Gehan  0.000 Site > Bkgd 0.0429 0.00116 0.0017 0.00088 23 54 61 148 43 Gehan  0.112 nsd 0.00108 0.000161 0.00108 0.000138 2 21 30 146 10 Gehan  0.658 nsd 0.00143 0.0013 0.00135 0.00074 6 21 138 147 29 Gehan  0.224 nsd 0.0044 0.00162 0.00245 0.00078 10 21 147 148 48 Gehan  0.215 nsd 0.00073 0.00013 0.00073 0.000105 1 21 16 147 5 Gehan  0.246 nsd 0.00055 7.71E‐05 0.00055 0.000069 1 21 23 147 5 Gehan  0.235 nsd 0.00055 0.000171 0.00055 0.000135 1 21 20 148 5 Gehan  0.253 nsd 0.0005 0.000156 0.0005 0.00013 1 21 24 147 5 Gehan  0.166 nsd 0.000785 0.000212 0.000785 0.000145 2 21 69 145 10 Gehan  0.181 nsd 0.00058 0.000132 0.00058 0.000125 1 21 11 148 5 Gehan  0.303 nsd 0.00047 8.18E‐05 0.00047 0.000072 1 21 50 145 5 Gehan  0.016 Site > Bkgd 0.00179 0.000175 0.00104 0.00015 4 21 66 144 19 Gehan  0.961 nsd 0.0395 0.0192 0.0395 0.019 2 54 53 141 4 Gehan  0.986 nsd 0.00325 0.0246 0.00125 0.017 6 54 51 148 11 Gehan  0.506 nsd 0.00597 0.0152 0.00597 0.0152 1 54 1 148 2 Gehan  0.567 nsd 0.00141 0.00856 0.0013 0.0085 5 54 5 145 9 Gehan  0.047 Site > Bkgd 0.0377 0.00646 0.0096 0.0064 3 54 6 141 6 Individual Criteria  Comparisons Number of  Samples   Percent  Exceeding  Detects  Background 95‐ Bkgd 95UTL 32 2 93 13 5 3 6 9 67 13 2 0 3 1 ‐‐ 1 3 1 4 6 76 14 11 1 18 2 41 11 21 2 94 0 99 2 11 1 16 1 14 1 16 1 48 2 7 1 34 1 46 4 38 2 34 0 1 0 3 0 4 2 Notes: ‐‐ = not available UTL = upper threshold limit WRS = Wilcoxon Rank Sum EN0411151012BAO  PAGE 6 OF 6 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Depth   Matrix Interval Measured Data Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft EN0411151012BAO  ERA Class Inorganics Inorganics ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Preferred Analyte Name Units Cyanides Tin Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1262 Aroclor 1268 Aroclor 5432 Aroclor 5442 Aroclor 5460 1,2‐Diphenylhydrazine 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐Dinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,6‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX Tetryl sym‐Trinitrobenzene 2,4,5‐T 2,4‐Dichlorophenoxyacetic Acid (2,4‐ Dalapon Dicamba mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 4 20 20 20 20 20 17 17 1 1 1 3 11 11 14 11 14 11 11 11 11 11 11 11 14 11 11 11 11 11 9 9 9 9 0.1626 0.564 0.00712 0.00712 0.00712 0.00712 0.00712 0.00712 0.00712 0.0356 0.0356 0.0356 0.07 0.3 0.3 0.3 1.1 0.07 1.1 0.3 0.3 0.3 0.3 0.3 0.3 0.07 3.6 1 0.3 0.3 0.3 0.0034 0.0107 0.18 0.0107 0.4 7.32 0.106 0.106 0.106 0.106 0.184 0.044 0.044 0.0356 0.0356 0.0356 0.362 0.76 0.76 0.76 1.5 0.76 1.5 0.76 0.76 0.76 0.76 0.76 1 0.76 5 5 0.76 0.76 0.76 0.0038 0.082 0.2 0.028 0.172 1.84 0.0196 0.0202 0.0196 0.0196 0.0233 0.0159 0.0159 0.0178 0.0178 0.0178 0.0843 0.296 0.296 0.272 0.619 0.251 0.619 0.296 0.296 0.296 0.296 0.296 0.389 0.251 2.06 1.92 0.296 0.296 0.296 0.00178 0.0338 0.0931 0.0117 0.18 31 0.12 0.18 0.082 0.043 0.0064 ‐‐ ‐‐ ‐‐ ‐‐ 0.039 n/a 0.92 0.13 ‐‐ ‐‐ ‐‐ ‐‐ 0.006 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ n/a 4.8 1.1 39 14 No No No No No No Yes ‐‐ ‐‐ ‐‐ ‐‐ No n/a No Yes ‐‐ ‐‐ ‐‐ ‐‐ Yes ‐‐ ‐‐ ‐‐ ‐‐ No ‐‐ ‐‐ ‐‐ No ‐‐ n/a No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0 ‐‐ ‐‐ ‐‐ ‐‐ 0 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 1 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft EN0411151012BAO  ERA Class Herbicides Herbicides Herbicides Herbicides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC Preferred Analyte Name Dichlorprop Dinoseb MCPP Silvex Aldrin Chlordane Dieldrin Endosulfan II Endrin ketone Heptachlor Methoxychlor Toxaphene alpha‐BHC delta‐BHC gamma‐BHC 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol Carbazole Dibenzofuran Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 9 9 9 13 13 13 13 13 13 13 13 13 13 13 3 3 3 3 3 3 1 3 3 3 3 3 3 3 3 3 2 3 3 3 3 0.0107 0.0107 2.14 0.0034 0.001422 0.01778 0.00284 0.00284 0.00284 0.001422 0.0134 0.0356 0.001422 0.001422 0.001422 0.07 0.07 0.07 0.07 0.722 0.0362 0.07 0.07 0.07 0.362 0.36 0.362 0.07 0.07 0.362 0.362 0.362 0.722 0.362 0.0362 0.07 0.038 0.054 5.6 0.0038 0.0166 0.34 0.034 0.034 0.036 0.0166 0.134 0.66 0.0166 0.0166 0.0166 0.362 0.362 0.362 0.362 2.2 0.072 0.07 0.362 0.362 0.74 0.362 1.1 0.362 0.362 1.1 1.1 7.4 1.1 1.1 0.074 0.362 0.0164 0.0227 2.42 0.00178 0.00144 0.0334 0.00298 0.00295 0.00311 0.00201 0.0117 0.0563 0.00144 0.00144 0.00144 0.0843 0.0843 0.0843 0.0843 0.854 0.0297 0.035 0.0843 0.0843 0.3 0.18 0.42 0.0843 0.0843 0.42 0.42 1.94 0.48 0.42 0.03 0.0843 0.79 0.18 2.5 0.55 0.057 1.1 0.013 0.22 0.0086 0.087 n/a 5.8 0.073 0.067 0.075 75 75 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ n/a ‐‐ n/a n/a n/a 8 ‐‐ ‐‐ 4.5 4.5 1.5 1.2 No No No No No No No No No No n/a No No No No No No ‐‐ No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ n/a ‐‐ n/a n/a n/a No ‐‐ ‐‐ No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 2 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft EN0411151012BAO  ERA Class SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name Units Dimethyl phthalate Diphenylamine Formaldehyde Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone Isopropanol Pentachlorophenol Phenol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether n‐Nitrosodi‐n‐propylamine n‐Nitrosodimethylamine n‐Nitrosodiphenylamine o‐Cresol p‐Chloro‐m‐cresol p‐Chloroaniline p‐Cresol p‐Nitroaniline 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trichlorobenzene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 31 1 13 3 18 3 3 3 3 3 3 3 3 3 3 31 2 3 3 3 3 3 18 19 19 19 19 19 19 17 17 17 18 18 18 17 0.0342 0.362 4 0.036 0.001834 0.362 0.36 0.07 2.4 0.36 0.07 0.07 0.07 0.07 0.07 0.0034 0.07 0.07 0.07 0.07 0.07 0.36 0.00168 0.001834 0.001834 0.0084 0.001834 0.001834 0.001834 0.001834 0.001834 0.00168 0.001834 0.001834 0.001834 0.001834 0.8 0.362 9.4 0.362 0.07 1.1 0.362 0.362 2.6 0.38 0.362 0.362 0.362 0.362 0.362 0.8 0.074 0.362 0.362 0.362 0.362 0.362 0.044 0.02 0.012 0.044 0.012 0.012 0.012 0.012 0.012 0.012 0.07 0.044 0.044 0.012 0.0377 0.181 2.39 0.0727 0.00525 0.42 0.18 0.0843 1.27 0.184 0.0843 0.0843 0.0843 0.0843 0.0843 0.0252 0.036 0.0843 0.0843 0.0843 0.0843 0.18 0.00286 0.00273 0.00247 0.00605 0.00247 0.00247 0.00366 0.00217 0.0035 0.00173 0.00525 0.00327 0.00453 0.00217 4.5 n/a 43 ‐‐ 0.022 3 ‐‐ ‐‐ ‐‐ 2.8 5.1 ‐‐ n/a n/a n/a 6.5 2.3 4.3 1.7 n/a 4.3 3.4 38 2460 51 220 9 78 6.9 ‐‐ 10 ‐‐ 10 3.1 0.28 12 No n/a No ‐‐ No No ‐‐ ‐‐ ‐‐ No No ‐‐ n/a n/a n/a No No No No n/a No No No No No No No No No ‐‐ No ‐‐ No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 3 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft EN0411151012BAO  ERA Class VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethanol Ethylbenzene Methanol Methyl ethyl ketone Methyl isobutyl ketone (MIBK) Methyl tert‐butyl ether Tetrachloroethene Toluene Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20 19 19 18 20 17 20 12 18 17 19 19 17 17 19 19 19 19 19 19 19 19 12 17 18 17 18 3 3 19 3 18 17 17 19 19 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.0084 0.00916 0.00916 0.00916 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.00168 0.001834 0.001834 0.001834 0.001834 0.0084 0.001834 0.001834 0.00168 0.001834 0.01 2.4 0.001834 2.4 0.00916 0.0084 0.001834 0.001834 0.001834 0.07 0.012 0.012 0.044 0.07 0.012 0.07 0.044 0.108 0.022 0.108 0.012 0.012 0.012 0.012 0.02 0.022 0.012 0.012 0.022 0.02 0.022 0.044 0.012 0.012 0.012 0.022 0.012 2.6 0.012 2.6 0.108 0.022 0.012 0.012 0.012 0.00439 0.00247 0.00247 0.00327 0.00439 0.00217 0.00439 0.00631 0.0274 0.00804 0.0131 0.00247 0.0035 0.0035 0.00247 0.00392 0.00398 0.00207 0.00247 0.00398 0.00273 0.00398 0.00631 0.00217 0.00233 0.00173 0.00392 0.00533 1.27 0.00247 1.27 0.0106 0.00583 0.0035 0.00247 0.00247 130 78 33 3.2 23 ‐‐ 5.6 ‐‐ 160 23 46 73 25 ‐‐ 10 23 3.2 35 21 ‐‐ 69 3.2 ‐‐ 1.3 29 27 41 n/a ‐‐ 79 ‐‐ 8160 4.5 n/a 2.2 59 No No No No No ‐‐ No ‐‐ No No No No No ‐‐ No No No No No ‐‐ No No ‐‐ No No No No n/a ‐‐ No ‐‐ No No n/a No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 4 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  ERA Class VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Inorganics Inorganics ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL Energetics Energetics Energetics Energetics Energetics Preferred Analyte Name Trichloroethene Trichlorofluoromethane Vinyl chloride cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Cyanides Tin Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1262 Aroclor 1268 Aroclor 5432 Aroclor 5442 Aroclor 5460 1,2‐Diphenylhydrazine 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐Dinitrotoluene 2,4‐diamino‐6‐nitrotoluene Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 19 19 19 19 19 17 17 17 18 17 17 17 17 3 3 3 17 19 19 9 4 20 20 20 20 20 17 17 1 1 1 3 11 11 14 11 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.00168 0.01 0.102 0.01 0.001834 0.001834 0.001834 0.1626 0.564 0.00712 0.00712 0.00712 0.00712 0.00712 0.00712 0.00712 0.0356 0.0356 0.0356 0.07 0.3 0.3 0.3 1.1 0.012 0.012 0.022 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.11 0.012 0.012 0.012 0.012 0.4 7.32 0.106 0.106 0.106 0.106 0.184 0.044 0.044 0.0356 0.0356 0.0356 0.362 0.76 0.76 0.76 1.5 0.00247 0.00366 0.00278 0.00247 0.00247 0.0035 0.00217 0.0035 0.00266 0.0035 0.00217 0.0035 0.00173 0.00533 0.0537 0.00533 0.0035 0.00247 0.00247 0.172 1.84 0.0196 0.0202 0.0196 0.0196 0.0233 0.0159 0.0159 0.0178 0.0178 0.0178 0.0843 0.296 0.296 0.272 0.619 1.8 170 0.78 210 n/a 61 73 16 n/a 16 3.7 0.98 n/a n/a n/a n/a 1.1 130 ‐‐ 0.18 31 0.12 0.18 0.082 0.043 0.0064 ‐‐ ‐‐ ‐‐ ‐‐ 0.039 n/a 0.92 0.13 ‐‐ ‐‐ No No No No n/a No No No n/a No No No n/a n/a n/a n/a No No ‐‐ No No No No No No Yes ‐‐ ‐‐ ‐‐ ‐‐ No n/a No Yes ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0 ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No Yes No No No No No No No No No No PAGE 5 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  ERA Class Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC Preferred Analyte Name Units 2,6‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX Tetryl sym‐Trinitrobenzene 2,4,5‐T 2,4‐Dichlorophenoxyacetic Acid (2,4‐ Dalapon Dicamba Dichlorprop Dinoseb MCPP Silvex Aldrin Chlordane Dieldrin Endosulfan II Endrin ketone Heptachlor Methoxychlor Toxaphene alpha‐BHC delta‐BHC gamma‐BHC 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 14 11 11 11 11 11 11 11 14 11 11 11 11 11 9 9 9 9 9 9 9 9 13 13 13 13 13 13 13 13 13 13 13 3 3 3 0.07 1.1 0.3 0.3 0.3 0.3 0.3 0.3 0.07 3.6 1 0.3 0.3 0.3 0.0034 0.0107 0.18 0.0107 0.0107 0.0107 2.14 0.0034 0.001422 0.01778 0.00284 0.00284 0.00284 0.001422 0.0134 0.0356 0.001422 0.001422 0.001422 0.07 0.07 0.07 0.76 1.5 0.76 0.76 0.76 0.76 0.76 1 0.76 5 5 0.76 0.76 0.76 0.0038 0.082 0.2 0.028 0.038 0.054 5.6 0.0038 0.0166 0.34 0.034 0.034 0.036 0.0166 0.134 0.66 0.0166 0.0166 0.0166 0.362 0.362 0.362 0.251 0.619 0.296 0.296 0.296 0.296 0.296 0.389 0.251 2.06 1.92 0.296 0.296 0.296 0.00178 0.0338 0.0931 0.0117 0.0164 0.0227 2.42 0.00178 0.00144 0.0334 0.00298 0.00295 0.00311 0.00201 0.0117 0.0563 0.00144 0.00144 0.00144 0.0843 0.0843 0.0843 ‐‐ ‐‐ 0.006 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ n/a 4.8 1.1 39 14 0.79 0.18 2.5 0.55 0.057 1.1 0.013 0.22 0.0086 0.087 n/a 5.8 0.073 0.067 0.075 75 75 ‐‐ ‐‐ ‐‐ Yes ‐‐ ‐‐ ‐‐ ‐‐ No ‐‐ ‐‐ ‐‐ No ‐‐ n/a No No No No No No No No No No No No No No n/a No No No No No No ‐‐ ‐‐ ‐‐ 0 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 6 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  ERA Class SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC Preferred Analyte Name 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol Carbazole Dibenzofuran Dimethyl phthalate Diphenylamine Formaldehyde Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone Isopropanol Pentachlorophenol Phenol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether n‐Nitrosodi‐n‐propylamine n‐Nitrosodimethylamine n‐Nitrosodiphenylamine o‐Cresol Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 3 3 1 3 3 3 3 3 3 3 3 3 2 3 3 3 3 32 1 13 3 19 3 3 3 3 3 3 3 3 3 3 32 2 3 0.07 0.722 0.0362 0.07 0.07 0.07 0.362 0.36 0.362 0.07 0.07 0.362 0.362 0.362 0.722 0.362 0.0362 0.07 0.0342 0.362 4 0.036 0.001834 0.362 0.36 0.07 2.4 0.36 0.07 0.07 0.07 0.07 0.07 0.0034 0.07 0.07 0.362 2.2 0.072 0.07 0.362 0.362 0.74 0.362 1.1 0.362 0.362 1.1 1.1 7.4 1.1 1.1 0.074 0.362 0.8 0.362 9.4 0.362 0.07 1.1 0.362 0.362 2.6 0.38 0.362 0.362 0.362 0.362 0.362 0.8 0.074 0.362 0.0843 0.854 0.0297 0.035 0.0843 0.0843 0.3 0.18 0.42 0.0843 0.0843 0.42 0.42 1.94 0.48 0.42 0.03 0.0843 0.0372 0.181 2.39 0.0727 0.00524 0.42 0.18 0.0843 1.27 0.184 0.0843 0.0843 0.0843 0.0843 0.0843 0.0245 0.036 0.0843 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ n/a ‐‐ n/a n/a n/a 8 ‐‐ ‐‐ 4.5 4.5 1.5 1.2 4.5 n/a 43 ‐‐ 0.022 3 ‐‐ ‐‐ ‐‐ 2.8 5.1 ‐‐ n/a n/a n/a 6.5 2.3 4.3 No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ n/a ‐‐ n/a n/a n/a No ‐‐ ‐‐ No No No No No n/a No ‐‐ No No ‐‐ ‐‐ ‐‐ No No ‐‐ n/a n/a n/a No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 7 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  ERA Class SVOC SVOC SVOC SVOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name Units p‐Chloro‐m‐cresol p‐Chloroaniline p‐Cresol p‐Nitroaniline 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trichlorobenzene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Acetone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 3 3 3 19 20 20 20 20 20 20 18 18 18 19 19 19 18 21 20 20 19 21 18 21 13 19 18 20 20 18 18 20 20 20 20 0.07 0.07 0.07 0.36 0.00168 0.001834 0.001834 0.0084 0.001834 0.001834 0.001834 0.001834 0.001834 0.00168 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.0084 0.00916 0.00916 0.00916 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.00168 0.362 0.362 0.362 0.362 0.044 0.02 0.012 0.044 0.012 0.012 0.012 0.012 0.012 0.012 0.07 0.044 0.044 0.012 0.07 0.012 0.012 0.044 0.07 0.012 0.07 0.044 0.108 0.022 0.108 0.012 0.012 0.012 0.012 0.02 0.022 0.012 0.0843 0.0843 0.0843 0.18 0.00297 0.00284 0.00259 0.006 0.00259 0.00259 0.00373 0.00233 0.00359 0.00191 0.00524 0.00336 0.00456 0.00233 0.00442 0.00259 0.00259 0.00336 0.00442 0.00233 0.00442 0.00621 0.0264 0.00815 0.0135 0.00259 0.00359 0.00359 0.00259 0.00398 0.00403 0.00222 1.7 n/a 4.3 3.4 38 2460 51 220 9 78 6.9 ‐‐ 10 ‐‐ 10 3.1 0.28 12 130 78 33 3.2 23 ‐‐ 5.6 ‐‐ 160 23 46 73 25 ‐‐ 10 23 3.2 35 No n/a No No No No No No No No No ‐‐ No ‐‐ No No No No No No No No No ‐‐ No ‐‐ No No No No No ‐‐ No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 8 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft 0‐4 ft EN0411151012BAO  ERA Class VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethanol Ethylbenzene Methanol Methyl ethyl ketone Methyl isobutyl ketone (MIBK) Methyl tert‐butyl ether Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Vinyl chloride cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene trans‐1,2‐Dichloroethene Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20 20 20 20 13 18 19 18 19 4 3 20 3 19 18 18 20 20 20 20 20 20 20 18 18 18 19 18 18 18 18 4 4 4 18 20 0.001834 0.001834 0.001834 0.001834 0.0084 0.001834 0.001834 0.00168 0.001834 0.01 2.4 0.001834 2.4 0.00916 0.0084 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.001834 0.00168 0.01 0.102 0.01 0.001834 0.001834 0.012 0.022 0.02 0.022 0.044 0.012 0.012 0.012 0.022 0.012 2.6 0.012 2.6 0.108 0.022 0.012 0.012 0.012 0.012 0.012 0.022 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.11 0.012 0.012 0.012 0.00259 0.00403 0.00284 0.00403 0.00621 0.00233 0.00247 0.00191 0.00398 0.00525 1.27 0.00259 1.27 0.0106 0.00606 0.00359 0.00259 0.00259 0.00259 0.00373 0.00289 0.00259 0.00259 0.00359 0.00233 0.00359 0.00279 0.00359 0.00233 0.00359 0.00191 0.00525 0.0533 0.00525 0.00359 0.00259 21 ‐‐ 69 3.2 ‐‐ 1.3 29 27 41 n/a ‐‐ 79 ‐‐ 8160 4.5 n/a 2.2 59 1.8 170 0.78 210 n/a 61 73 16 n/a 16 3.7 0.98 n/a n/a n/a n/a 1.1 130 No ‐‐ No No ‐‐ No No No No n/a ‐‐ No ‐‐ No No n/a No No No No No No n/a No No No n/a No No No n/a n/a n/a n/a No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 9 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐4 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  ERA Class VOC Inorganics ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL ARCL Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Energetics Herbicides Herbicides Herbicides Herbicides Herbicides Herbicides Preferred Analyte Name Units trans‐1,3‐Dichloropropene Cyanides Aroclor 1016 Aroclor 1221 Aroclor 1232 Aroclor 1242 Aroclor 1248 Aroclor 1262 Aroclor 1268 Aroclor 5432 Aroclor 5442 1,2‐Diphenylhydrazine 1,3‐Dinitrobenzene 2,4,6‐Trinitrotoluene 2,4‐Dinitrotoluene 2,4‐diamino‐6‐nitrotoluene 2,6‐Dinitrotoluene 2,6‐diamino‐4‐nitrotoluene 2‐Amino‐4,6‐Dinitrotoluene 2‐Nitrotoluene 3‐Nitrotoluene 4‐Amino‐2,6‐Dinitrotoluene 4‐Nitrotoluene HMX Nitrobenzene Nitroglycerin PETN RDX Tetryl sym‐Trinitrobenzene 2,4,5‐T 2,4‐Dichlorophenoxyacetic Acid (2,4‐ Dalapon Dicamba Dichlorprop Dinoseb mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20 15 33 33 33 33 33 30 30 3 3 4 19 19 23 19 23 19 19 19 19 19 19 19 23 19 19 19 19 19 15 15 15 15 15 15 0.001834 0.1626 0.00712 0.00712 0.00712 0.00712 0.00712 0.00712 0.00712 0.0356 0.0356 0.07 0.298 0.298 0.298 1.1 0.07 1.1 0.298 0.298 0.298 0.298 0.298 0.298 0.07 2 0.996 0.298 0.298 0.298 0.0034 0.0107 0.18 0.0107 0.0107 0.0107 0.012 0.46 0.106 0.106 0.106 0.106 0.184 0.044 0.044 0.0406 0.0406 0.362 0.76 0.76 0.76 1.5 0.76 1.5 0.76 0.76 0.76 0.76 0.76 1 0.76 5 5 0.76 0.76 0.76 0.0044 0.082 0.24 0.028 0.038 0.054 0.00259 0.176 0.0185 0.0189 0.0185 0.0185 0.0208 0.0163 0.0163 0.0187 0.0187 0.0725 0.293 0.293 0.273 0.636 0.254 0.636 0.293 0.293 0.293 0.293 0.293 0.382 0.254 2.06 1.86 0.293 0.293 0.293 0.00183 0.0315 0.0965 0.0113 0.0155 0.0214 ‐‐ 0.18 0.12 0.18 0.082 0.043 0.0064 ‐‐ ‐‐ ‐‐ ‐‐ n/a 0.92 0.13 ‐‐ ‐‐ ‐‐ ‐‐ 0.006 ‐‐ ‐‐ ‐‐ ‐‐ 110 ‐‐ ‐‐ ‐‐ 0.3 ‐‐ n/a 4.8 1.1 39 14 0.79 0.18 ‐‐ No No No No No Yes ‐‐ ‐‐ ‐‐ ‐‐ n/a No Yes ‐‐ ‐‐ ‐‐ ‐‐ Yes ‐‐ ‐‐ ‐‐ ‐‐ No ‐‐ ‐‐ ‐‐ No ‐‐ n/a No No No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0 ‐‐ ‐‐ ‐‐ ‐‐ 0 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 10 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  ERA Class Herbicides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC Preferred Analyte Name MCPP Aldrin Chlordane Dieldrin Endosulfan II Endrin ketone Methoxychlor Toxaphene alpha‐BHC delta‐BHC gamma‐BHC 2,4,5‐Trichlorophenol 2,4,6‐Trichlorophenol 2,4‐Dichlorophenol 2,4‐Dimethylphenol 2,4‐Dinitrophenol 2‐Chloronaphthalene 2‐Chlorophenol 2‐Nitroaniline 2‐Nitrophenol 3,3'‐Dichlorobenzidine 3,5‐Dimethylphenol 3‐Nitroaniline 4,6‐Dinitro‐o‐cresol 4‐Bromophenyl phenyl ether 4‐Chlorophenylphenyl ether 4‐Nitrophenol Aniline Benzidine Benzoic acid Benzyl alcohol Carbazole Dibenzofuran Dimethyl phthalate Diphenylamine Formaldehyde Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 15 21 21 21 21 21 21 21 21 21 21 4 4 4 4 4 4 2 4 4 4 1 4 4 4 4 4 4 3 4 4 4 4 54 1 22 2.14 0.001422 0.01778 0.00284 0.00284 0.00284 0.0134 0.0356 0.001422 0.001422 0.001422 0.07 0.07 0.07 0.07 0.722 0.0362 0.07 0.07 0.07 0.362 0.38 0.36 0.362 0.07 0.07 0.362 0.362 0.362 0.722 0.362 0.0362 0.07 0.0342 0.362 4 5.6 0.0166 0.34 0.034 0.034 0.036 0.134 0.66 0.0166 0.0166 0.0166 0.362 0.362 0.362 0.362 2.2 0.074 0.074 0.362 0.362 0.74 0.38 0.38 1.12 0.362 0.362 1.12 1.12 7.4 1.12 1.12 0.074 0.362 0.8 0.362 9.4 2.33 0.00123 0.0269 0.00252 0.0025 0.00264 0.0101 0.0471 0.00123 0.00123 0.00123 0.0725 0.0725 0.0725 0.0725 0.915 0.0315 0.036 0.0725 0.0725 0.318 0.19 0.183 0.455 0.0725 0.0725 0.455 0.455 2.53 0.5 0.455 0.0318 0.0725 0.0379 0.181 2.33 2.5 0.057 1.1 0.013 0.22 0.0086 n/a 5.8 0.073 0.067 0.075 75 75 ‐‐ 65 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ n/a 2.6 ‐‐ n/a n/a n/a 8 ‐‐ ‐‐ 4.5 4.5 1.5 1.2 4.5 n/a 43 No No No No No No n/a No No No No No No ‐‐ No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ n/a No ‐‐ n/a n/a n/a No ‐‐ ‐‐ No No No No No n/a No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 11 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  ERA Class SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC SVOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name Units Hexachlorobenzene Hexachlorobutadiene Hexachlorocyclopentadiene Hexachloroethane Isophorone Isopropanol Pentachlorophenol Phenol bis(2‐Chloroethoxy)methane bis(2‐Chloroethyl) ether bis(2‐Chloroisopropyl) ether n‐Nitrosodi‐n‐propylamine n‐Nitrosodimethylamine n‐Nitrosodiphenylamine o‐Cresol p‐Chloro‐m‐cresol p‐Chloroaniline p‐Cresol p‐Nitroaniline 1,1,1,2‐Tetrachloroethane 1,1,1‐Trichloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloro‐1,2,2‐trifluoroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,1‐Dichloropropene 1,2,3‐Trichlorobenzene 1,2,3‐Trichloropropane 1,2,4‐Trichlorobenzene 1,2,4‐Trimethylbenzene 1,2‐Dibromo‐3‐chloropropane 1,2‐Dibromoethane 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,2‐Dichloropropane mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4 33 4 4 4 6 4 4 4 4 4 4 54 3 4 4 4 4 4 33 34 34 34 34 34 34 31 31 31 33 33 33 31 36 34 34 0.036 0.001828 0.362 0.36 0.07 2.2 0.36 0.07 0.07 0.07 0.07 0.07 0.0034 0.07 0.07 0.07 0.07 0.07 0.36 0.00168 0.001828 0.001828 0.0084 0.001828 0.001828 0.001828 0.001828 0.001828 0.00168 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.362 0.074 1.12 0.38 0.362 2.6 0.38 0.362 0.362 0.362 0.362 0.362 0.8 0.074 0.362 0.362 0.362 0.362 0.38 0.044 0.02 0.012 0.044 0.012 0.012 0.012 0.012 0.012 0.012 0.074 0.044 0.044 0.012 0.074 0.012 0.012 0.0593 0.00546 0.455 0.183 0.0725 1.22 0.185 0.0725 0.0725 0.0725 0.0725 0.0725 0.0176 0.0363 0.0725 0.0725 0.0725 0.0725 0.183 0.00313 0.00271 0.00257 0.0062 0.00257 0.00257 0.00365 0.0023 0.00349 0.00191 0.00546 0.00349 0.00461 0.0023 0.00473 0.00257 0.00257 ‐‐ 0.022 3 ‐‐ ‐‐ ‐‐ 2.8 5.1 ‐‐ n/a n/a n/a 6.5 2.3 4.3 1.7 n/a 4.3 3.4 38 2460 51 220 9 78 6.9 ‐‐ 10 ‐‐ 10 3.1 0.28 12 130 78 33 ‐‐ No No ‐‐ ‐‐ ‐‐ No No ‐‐ n/a n/a n/a No No No No n/a No No No No No No No No No ‐‐ No ‐‐ No No No No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 12 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil  Depth  Interval 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft EN0411151012BAO  ERA Class VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name 1,3,5‐Trimethylbenzene 1,3‐Dichlorobenzene 1,3‐Dichloropropane 1,4‐Dichlorobenzene 2‐Chloro‐1,1,1‐trifluoroethane 2‐Chloroethylvinyl ether 2‐Hexanone Benzene Bromobenzene Bromochloromethane Bromodichloromethane Bromoform Bromomethane Carbon Tetrachloride Chlorobenzene Chloroethane Chloroform Chloromethane Chlorotrifluoroethylene Cumene Dibromochloromethane Dibromomethane Dichlorodifluoromethane Diisopropyl ether Ethanol Methanol Methyl ethyl ketone Methyl isobutyl ketone (MIBK) Methyl tert‐butyl ether Tetrachloroethene Toluene Trichloroethene Trichlorofluoromethane Vinyl chloride cis‐1,2‐Dichloroethene cis‐1,3‐Dichloropropene Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 33 36 31 36 23 33 31 34 31 31 34 34 34 34 34 34 34 34 23 31 32 31 33 6 6 6 33 31 31 34 34 34 34 34 34 34 0.001828 0.001828 0.001828 0.001828 0.0084 0.00914 0.00914 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.00168 0.001828 0.001828 0.001828 0.001828 0.0084 0.001828 0.001828 0.00168 0.001828 0.01 2.2 2.2 0.00914 0.0084 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.044 0.074 0.012 0.074 0.044 0.112 0.022 0.012 0.012 0.012 0.012 0.024 0.022 0.012 0.012 0.022 0.024 0.022 0.044 0.012 0.012 0.012 0.022 0.012 2.6 2.6 0.112 0.022 0.012 0.012 0.012 0.012 0.012 0.022 0.012 0.012 0.00349 0.00473 0.0023 0.00473 0.00636 0.0268 0.00807 0.00257 0.00349 0.00349 0.00257 0.00398 0.00396 0.00221 0.00257 0.00396 0.00289 0.00398 0.00636 0.0023 0.00238 0.00191 0.00395 0.00517 1.22 1.22 0.0109 0.00609 0.00349 0.00257 0.00257 0.00257 0.00365 0.00289 0.00257 0.00257 3.2 23 ‐‐ 5.6 ‐‐ 160 23 73 25 ‐‐ 10 23 3.2 35 21 ‐‐ 69 3.2 ‐‐ 1.3 29 27 41 n/a ‐‐ ‐‐ 8160 4.5 n/a 2.2 59 1.8 170 0.78 210 n/a No No ‐‐ No ‐‐ No No No No ‐‐ No No No No No ‐‐ No No ‐‐ No No No No n/a ‐‐ ‐‐ No No n/a No No No No No No n/a ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No PAGE 13 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor Soil Vapor  Depth  Interval 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft ERA Class VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC SVOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC VOC Preferred Analyte Name n‐Butylbenzene n‐Propylbenzene o‐Chlorotoluene o‐Xylene p‐Chlorotoluene p‐Cymene sec‐Butylbenzene sec‐Dichloropropane tert‐Amyl methyl ether tert‐Butyl alcohol tert‐Butyl ethyl ether tert‐Butylbenzene trans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene Isopropanol 1,1,1,2‐Tetrachloroethane 1,1,2,2‐Tetrachloroethane 1,1,2‐Trichloroethane 1,1‐Dichloroethane 1,1‐Dichloroethene 1,2‐Dichlorobenzene 1,2‐Dichloroethane 1,3‐Dichloropropane 1,4‐Dichlorobenzene Carbon Tetrachloride Chloroethane Methylene chloride Vinyl chloride cis‐1,2‐Dichloroethene trans‐1,2‐Dichloroethene Units mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  mg/Kg  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  ug/L  Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 31 31 31 33 31 31 31 31 6 6 6 31 34 34 13 25 25 25 25 25 13 25 13 13 25 25 25 25 25 25 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.001828 0.00168 0.01 0.098 0.01 0.001828 0.001828 0.001828 10 0.0138 0.0138 0.011 0.008 0.008 0.2 0.008 0.2 0.2 0.0126 0.0052 0.007 0.0052 0.008 0.008 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.012 0.11 0.012 0.012 0.012 0.012 10 2 2 2 2 2 0.2 2 0.2 0.2 2 2 10 2 2 2 0.00349 0.0023 0.00349 0.00268 0.00349 0.0023 0.00349 0.00191 0.00517 0.0527 0.00517 0.00349 0.00257 0.00257 5 0.237 0.265 0.309 0.237 0.237 0.1 0.237 0.1 0.1 0.235 0.309 1.65 0.235 0.237 0.237 61 73 16 n/a 16 3.7 0.98 n/a n/a n/a n/a 1.1 130 ‐‐ ‐‐ ‐‐ ‐‐ 1.1 240 7.9 66 56 n/a n/a 8.4 1320 12 0.73 25 25 No No No n/a No No No n/a n/a n/a n/a No No ‐‐ ‐‐ ‐‐ ‐‐ No No No No No n/a n/a No No No No No No ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ No No No No No No No No No No No No No No No No No No No No No No No No No No No No No No Notes: a  Chemicals are retained as CPECs if the mean nondetect SQL exceeds the minimum Low EcoRBSL, there is a potential for historical site use, and there was at least 1 other chemical      from the same chemical class was detected in the specified depth interval. CPEC = chemical of potential ecological concern EN0411151012BAO  PAGE 14 OF 15 ATTACHMENT 1, TABLE 6 Evaluation of SQLs for Chemicals Never Detected RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Detection Level Evaluationa  Matrix  Depth  Interval ERA Class Preferred Analyte Name Units Number of  Analytes   Minimum  Mean Non  Detected in  Retained Number  Number  SQL for   Maximum  Same  Mean Detect SQL>  as a of  of  Non‐ SQL for Non‐ Non Detect  Minimm Low  Minimum  Chemical  CPECa? Detects Analyses detects Class? detects SQL EcoRBSL Low EcoRBSL ERA = ecological risk assessment ESL = ecological screening level  RBSL = risk‐based screening level SQL = sample quantitation limit EN0411151012BAO  PAGE 15 OF 15 ATTACHMENT 1, TABLE 7 Extrapolation of Aroclors to PCB Congeners in Soil ‐ RME RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California PCB Congener a b Extrapolation Factors /TEFs Aroclor‐1254 EF Aroclor‐1260 EF Mammal TEF Bird TEF RFI Site Soil  Horizon (ft  bgs) Chemical 77 1.5E‐02 1.3E‐02 1.0E‐04 5.0E‐02 81 3.0E‐03 2.3E‐03 3.0E‐04 1.0E‐01 105 1.2E‐01 8.2E‐02 3.0E‐05 1.0E‐04 114 4.5E‐03 1.5E‐03 3.0E‐05 1.0E‐04 RME  Concentration Units 0.0473 0.0473 0.0329 mg/kg mg/kg mg/kg 7.1E‐04 7.1E‐04 4.9E‐04 1.4E‐04 1.4E‐04 9.9E‐05 5.7E‐03 5.7E‐03 3.9E‐03 2.1E‐04 2.1E‐04 1.5E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 3.5E‐05 3.5E‐05 2.5E‐05 7.1E‐08 7.1E‐08 4.9E‐08 1.4E‐05 1.4E‐05 9.9E‐06 4.3E‐08 4.3E‐08 3.0E‐08 5.7E‐07 5.7E‐07 3.9E‐07 1.7E‐07 1.7E‐07 1.2E‐07 2.1E‐08 2.1E‐08 1.5E‐08 6.4E‐09 6.4E‐09 4.4E‐09 0.0379 0.0379 0.0105 mg/kg mg/kg mg/kg 4.9E‐04 4.9E‐04 1.4E‐04 8.7E‐05 8.7E‐05 2.4E‐05 3.1E‐03 3.1E‐03 8.6E‐04 5.7E‐05 5.7E‐05 1.6E‐05 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg 2.5E‐05 2.5E‐05 6.8E‐06 4.9E‐08 4.9E‐08 1.4E‐08 8.7E‐06 8.7E‐06 2.4E‐06 2.6E‐08 2.6E‐08 7.2E‐09 3.1E‐07 3.1E‐07 8.6E‐08 9.3E‐08 9.3E‐08 2.6E‐08 5.7E‐09 5.7E‐09 1.6E‐09 1.7E‐09 1.7E‐09 4.7E‐10 118 2.7E‐01 1.6E‐01 3.0E‐05 1.0E‐05 123 3.0E‐03 2.3E‐03 3.0E‐05 1.0E‐05 126 7.5E‐03 6.4E‐03 1.0E‐01 1.0E‐01 156 6.3E‐02 5.5E‐02 3.0E‐05 1.0E‐04 157 1.2E‐02 2.5E‐02 3.0E‐05 1.0E‐04 167 2.1E‐02 4.3E‐02 3.0E‐05 1.0E‐05 169 3.7E‐04 6.4E‐04 3.0E‐02 1.0E‐03 189 3.0E‐03 6.4E‐03 3.0E‐05 1.0E‐05 Total PCB‐TEQ Extrapolation Based on Aroclor‐1254 1 ‐ Convert Aroclor‐1254 to Congeners EEL 0‐2 Aroclor‐1254 EEL 0‐4 Aroclor‐1254 EEL 0‐6 Aroclor‐1254 2 ‐ Convert Congeners to TEQs EEL 0‐2 PCB_TEQ_Bird EEL 0‐4 PCB_TEQ_Bird EEL 0‐6 PCB_TEQ_Bird EEL 0‐2 PCB_TEQ_Mammal EEL 0‐4 PCB_TEQ_Mammal EEL 0‐6 PCB_TEQ_Mammal Extrapolated Congener Concentration 1.3E‐02 1.4E‐04 3.5E‐04 3.0E‐03 1.3E‐02 1.4E‐04 3.5E‐04 3.0E‐03 8.9E‐03 9.9E‐05 2.5E‐04 2.1E‐03 TCDD Toxicity Equivalents (PCB‐TEQ) 1.3E‐07 1.4E‐09 3.5E‐05 3.0E‐07 1.3E‐07 1.4E‐09 3.5E‐05 3.0E‐07 8.9E‐08 9.9E‐10 2.5E‐05 2.1E‐07 3.8E‐07 4.3E‐09 3.5E‐05 8.9E‐08 3.8E‐07 4.3E‐09 3.5E‐05 8.9E‐08 2.7E‐07 3.0E‐09 2.5E‐05 6.2E‐08 5.7E‐04 5.7E‐04 3.9E‐04 9.9E‐04 9.9E‐04 6.9E‐04 1.8E‐05 1.8E‐05 1.2E‐05 1.4E‐04 1.4E‐04 9.9E‐05 5.7E‐08 5.7E‐08 3.9E‐08 1.7E‐08 1.7E‐08 1.2E‐08 9.9E‐09 9.9E‐09 6.9E‐09 3.0E‐08 3.0E‐08 2.1E‐08 1.8E‐08 1.8E‐08 1.2E‐08 5.3E‐07 5.3E‐07 3.7E‐07 1.4E‐09 1.4E‐09 9.9E‐10 4.3E‐09 4.3E‐09 3.0E‐09 9.5E‐04 9.5E‐04 2.6E‐04 1.6E‐03 1.6E‐03 4.5E‐04 2.4E‐05 2.4E‐05 6.7E‐06 2.4E‐04 2.4E‐04 6.7E‐05 9.5E‐08 9.5E‐08 2.6E‐08 2.8E‐08 2.8E‐08 7.9E‐09 1.6E‐08 1.6E‐08 4.5E‐09 4.9E‐08 4.9E‐08 1.4E‐08 2.4E‐08 2.4E‐08 6.7E‐09 7.3E‐07 7.3E‐07 2.0E‐07 2.4E‐09 2.4E‐09 6.7E‐10 7.3E‐09 7.3E‐09 2.0E‐09 8.6E‐05 8.6E‐05 6.0E‐05 3.7E‐05 3.7E‐05 2.6E‐05 Extrapolation Based on Aroclor‐1260 1 ‐ Convert Aroclor‐1260 to Congeners EEL 0‐2 Aroclor‐1260 EEL 0‐4 Aroclor‐1260 EEL 0‐6 Aroclor‐1260 2 ‐ Convert Congeners to TEQs EEL 0‐2 PCB_TEQ_Bird EEL 0‐4 PCB_TEQ_Bird EEL 0‐6 PCB_TEQ_Bird EEL 0‐2 PCB_TEQ_Mammal EEL 0‐4 PCB_TEQ_Mammal EEL 0‐6 PCB_TEQ_Mammal Total PCB‐TEQs: EEL 0‐2 PCB_TEQ_Bird EEL 0‐2 PCB_TEQ_Mammal EEL 0‐4 PCB_TEQ_Bird EEL 0‐4 PCB_TEQ_Mammal EEL 0‐6 PCB_TEQ_Bird EEL 0‐6 PCB_TEQ_Mammal mg/kg mg/kg mg/kg mg/kg mg/kg mg/kg Extrapolated Congener Concentration 6.1E‐03 8.7E‐05 2.4E‐04 2.1E‐03 6.1E‐03 8.7E‐05 2.4E‐04 2.1E‐03 1.7E‐03 2.4E‐05 6.7E‐05 5.8E‐04 TCDD Toxicity Equivalents (PCB‐TEQ) 6.1E‐08 8.7E‐10 2.4E‐05 2.1E‐07 6.1E‐08 8.7E‐10 2.4E‐05 2.1E‐07 1.7E‐08 2.4E‐10 6.7E‐06 5.8E‐08 1.8E‐07 2.6E‐09 2.4E‐05 6.3E‐08 1.8E‐07 2.6E‐09 2.4E‐05 6.3E‐08 5.0E‐08 7.2E‐10 6.7E‐06 1.7E‐08 5.8E‐05 5.8E‐05 1.6E‐05 2.5E‐05 2.5E‐05 7.1E‐06 1.4E‐04 6.2E‐05 1.4E‐04 6.2E‐05 7.6E‐05 3.3E‐05 Notes: (a) Extrapolation factors are the maximum ratios of PCB congener to Aroclor concentration (MWH 2005) (b) TEFs are from Van den Berg 1998 and 2006. EEL = Environmental Effects Laboratory  EF = Aroclor to PCB congener extrapolation factor mg/kg = milligrams per kilogram  PCB = polychlorinated biphenyl TEF = 2,3,7,8‐Tetrachlorodibenzo‐p‐dioxin Equivalency Factor  TEQ = toxicity equivalent  EN0411151012BAO  PAGE 1 OF 1 ATTACHMENT1, TABLE 8 Identification of Soil Depth Interval for Small Mammals RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California   Deer Mouse  Soil From 0‐2 Feet Soil From 0‐4 Feet Soil From 0‐6 Feet Matri Chemical of Potential Ecological  Low EcoRBSL  Max Conc  Hazard  Max Conc  Max Conc  Hazard  x Type  ERAClass Concern (mg/kg) (mg/kg) Quotient (mg/kg) Hazard Quotient (mg/kg) Quotient Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil I I I I I I I O O O O O O O O O O O O O O O O O O O O O O O O O O O O O Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL ARCL Dioxin_Furans Herbicides Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides EN0411151012BAO  Perchlorate Antimony Arsenic Fluoride Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 DioxinFuran_TEQ_Mammal 2,4‐Dichlorophenoxybutyric acid MCPA Silvex Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde 0.5 0.042 2.1 140 7.3 ‐‐ 3.5 0.039 0.025 0.039 0.0000005 6.2 0.12 0.55 0.81 5.1 2.4 7.4 4.9 1.2 2.3 4.8 1.2 63 26 140 160 55 37 68 0.55 0.38 0.59 0.22 0.23 0.088 0.1 0.024 7.5 110 3.1 3.2 0.82 3.5 0.099 0.046 Not CPEC 0.0000519 0.032 0.94 Not CPEC 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.019 0.00073 0.00055 0.00055 0.0005 0.0011 4.8E‐02 1.8E+02 5.2E+01 2.2E‐02 4.4E‐01 0 1.0E+00 2.5E+00 1.8E+00 0 1.0E+02 5.2E‐03 7.8E+00 0 1.5E+00 1.5E‐01 4.2E‐01 3.1E‐02 1.1E‐01 1.3E+00 4.2E‐02 5.4E‐02 2.1E+00 2.7E‐04 8.1E‐05 9.3E‐04 1.4E‐02 2.7E‐04 5.9E‐05 1.3E‐02 3.3E‐03 5.0E‐02 1.2E‐03 2.5E‐03 2.4E‐03 5.7E‐03 1.1E‐02 0.024 7.5 110 3.1 3.2 0.82 3.5 0.099 0.046 Not CPEC 0.0000519 0.032 0.94 Not CPEC 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.019 0.00073 0.00055 0.00055 0.0005 0.0011 4.8E‐02 1.8E+02 5.2E+01 2.2E‐02 4.4E‐01 0 1.0E+00 2.5E+00 1.8E+00 0 1.0E+02 5.2E‐03 7.8E+00 0 1.5E+00 1.5E‐01 4.2E‐01 3.1E‐02 1.1E‐01 1.3E+00 4.2E‐02 5.4E‐02 2.1E+00 2.7E‐04 8.1E‐05 9.3E‐04 1.4E‐02 2.7E‐04 5.9E‐05 1.3E‐02 3.3E‐03 5.0E‐02 1.2E‐03 2.5E‐03 2.4E‐03 5.7E‐03 1.1E‐02 0.043 7.5 110 11.2 3.2 0.82 3.5 0.099 0.046 0.00706 0.0000519 0.032 0.94 0.0014 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.019 0.00073 0.00055 0.00055 0.0005 0.0011 8.6E‐02 1.8E+02 5.2E+01 8.0E‐02 4.4E‐01 0 1.0E+00 2.5E+00 1.8E+00 1.8E‐01 1.0E+02 5.2E‐03 7.8E+00 2.5E‐03 1.5E+00 1.5E‐01 4.2E‐01 3.1E‐02 1.1E‐01 1.3E+00 4.2E‐02 5.4E‐02 2.1E+00 2.7E‐04 8.1E‐05 9.3E‐04 1.4E‐02 2.7E‐04 5.9E‐05 1.3E‐02 3.3E‐03 5.0E‐02 1.2E‐03 2.5E‐03 2.4E‐03 5.7E‐03 1.1E‐02 PAGE 1 OF 2 ATTACHMENT1, TABLE 8 Identification of Soil Depth Interval for Small Mammals RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California   Deer Mouse  Soil From 0‐2 Feet Soil From 0‐4 Feet Soil From 0‐6 Feet Matri Chemical of Potential Ecological  Low EcoRBSL  Max Conc  Hazard  Max Conc  Max Conc  Hazard  x Type  ERAClass Concern (mg/kg) (mg/kg) Quotient (mg/kg) Hazard Quotient (mg/kg) Quotient Soil Soil Soil Soil Soil Soil Soil Soil Soil O O O O O O O O O Pesticides Pesticides Pesticides SVOC VOC VOC VOC VOC VOC Heptachlor Heptachlor epoxide Mirex Di‐n‐octyl phthalate Acetone Ethylbenzene Methylene chloride Styrene Xylenes, Total Total Hazard Index: Soil Depth Interval of Concern for Deer Mouse: 0-6 ft bgs 0.087 0.0013 0.12 94 46 41 27 210 3.4 Not CPEC 0.00047 0.0047 0.099 Not CPEC Not CPEC 0.0027 0.000723 0.000372 0 3.6E‐01 3.9E‐02 1.1E‐03 0 0 1.0E‐04 3.4E‐06 1.1E‐04 354.7 Not CPEC 0.00047 0.0047 0.099 Not CPEC Not CPEC 0.0027 0.000723 0.000372 0 3.6E‐01 3.9E‐02 1.1E‐03 0 0 1.0E‐04 3.4E‐06 1.1E‐04 354.7 0.00058 0.00047 0.0047 0.099 0.016 0.000312 0.00281 0.000723 0.00136 6.7E‐03 3.6E‐01 3.9E‐02 1.1E‐03 3.5E‐04 7.6E‐06 1.0E‐04 3.4E‐06 4.0E‐04 355.0 Notes: -- not available BHC = benzene hexachloride CPEC = chemical of potential ecological concern ERA = ecological risk assessment ft = feet  MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight PAH = polcyclic aromatic hydrocarbon SVOC = semivolatile organic compound VOC = volatile organic compound EN0411151012BAO  PAGE 2 OF 2 ATTACHMENT 1, TABLE 9 Summary of Hazard Quotients and Hazard Indices RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California 10 11 Hermit Thrush (0‐2 ft bgs)  Matrix Type Measured Data Soil I Soil I Soil I Soil I Soil I Soil I Soil I Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O Soil O EN0411151012BAO   ERAClass Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL ARCL ARCL Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Dioxin_Furans Herbicides Chemical of Potential Ecological Concern Perchlorate Antimony Arsenic Fluoride Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1248 Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 1,2,3,4,6,7,8‐Heptachlorodibenzofuran 1,2,3,4,6,7,8‐Heptachlorodibenzo‐p‐dioxin 1,2,3,4,7,8,9‐Heptachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzofuran 1,2,3,4,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,6,7,8‐Hexachlorodibenzofuran 1,2,3,6,7,8‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8,9‐Hexachlorodibenzo‐p‐dioxin 1,2,3,7,8‐Pentachlorodibenzofuran 1,2,3,7,8‐Pentachlorodibenzo‐p‐dioxin 2,3,4,6,7,8‐Hexachlorodibenzofuran 2,3,4,7,8‐Pentachlorodibenzofuran 2,3,7,8‐TCDD 2,3,7,8‐Tetrachlorodibenzofuran DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal Octachlorodibenzofuran Octachlorodibenzo‐p‐dioxin 2,4‐Dichlorophenoxybutyric acid 12 13 Deer Mouse (0‐6 ft bgs) Terrestrial  Soil  Low  High  Low  High  Plants Invertebrates EcoRBSL  EcoRBSL  EcoRBSL  EcoRBSL  (0‐2 ft bgs) (0‐2 ft bgs) HQ HQ HQ HQ 1E‐04 2E‐01 1E+00 ‐‐ 4E‐02 ‐‐ 1E‐03 6E‐04 1E‐03 9E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1E‐02 4E‐01 ‐‐ 3E+00 ‐‐ ‐‐ 5E‐05 9E‐05 8E‐05 ‐‐ 2E‐04 1E‐03 9E‐06 5E‐06 1E‐05 5E‐06 5E‐05 3E‐05 5E‐06 6E‐06 7E‐06 2E‐06 6E‐07 1E‐06 ‐‐ ‐‐ 6E‐04 2E‐02 ‐‐ 6E‐03 ‐‐ 7E‐01 ‐‐ ‐‐ ‐‐ 6E‐01 2E‐01 6E‐01 7E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2E+00 ‐‐ ‐‐ ‐‐ 2E‐04 2E‐03 ‐‐ 2E‐01 ‐‐ ‐‐ ‐‐ 2E‐02 2E‐02 6E‐02 7E‐02 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2E‐01 ‐‐ ‐‐ ‐‐ ‐‐ 2E‐02 1E+01 8E+00 2E‐02 1E‐01 ‐‐ 7E‐02 4E+00 8E‐01 4E‐01 2E‐01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3E+01 ‐‐ ‐‐ 4E‐03 2E‐03 3E‐01 5E‐01 1E‐02 3E‐02 ‐‐ 4E‐03 4E‐01 8E‐02 4E‐02 2E‐02 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 3E+00 ‐‐ ‐‐ 1E‐03 PAGE 1 OF 3 ATTACHMENT 1, TABLE 9 Summary of Hazard Quotients and Hazard Indices RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California 10 11 Hermit Thrush (0‐2 ft bgs)  Matrix Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil EN0411151012BAO  Type  ERAClass O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC VOC Chemical of Potential Ecological Concern MCPA Silvex Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex Silvex Di‐n‐octyl phthalate Acetone 12 13 Deer Mouse (0‐6 ft bgs) Terrestrial  Soil  Low  High  Low  High  Plants Invertebrates EcoRBSL  EcoRBSL  EcoRBSL  EcoRBSL  (0‐2 ft bgs) (0‐2 ft bgs) HQ HQ HQ HQ ‐‐ ‐‐ 3E‐01 1E‐01 3E‐01 5E‐02 2E‐01 4E‐01 9E‐03 6E‐02 8E‐01 6E‐04 1E‐04 3E‐02 4E‐01 6E‐03 2E‐05 2E‐01 2E‐04 5E‐04 7E‐07 6E‐07 6E‐07 ‐‐ ‐‐ ‐‐ 5E‐07 ‐‐ ‐‐ 9E‐05 ‐‐ ‐‐ ‐‐ 2E‐02 1E‐02 2E‐02 3E‐03 1E‐02 3E‐02 6E‐04 4E‐03 5E‐02 4E‐04 7E‐05 2E‐03 3E‐02 2E‐04 6E‐05 8E‐03 2E‐04 5E‐04 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 4E‐03 ‐‐ 2E‐02 1E‐03 5E‐03 3E‐04 2E‐03 1E‐02 2E‐04 ‐‐ 3E‐02 1E‐02 6E‐03 2E‐02 2E‐02 8E‐03 6E‐05 2E‐01 4E‐01 2E+00 1E‐03 4E‐05 4E‐05 6E‐02 1E‐01 ‐‐ 4E‐04 8E‐06 ‐‐ 1E‐03 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 1E‐03 6E‐04 2E‐03 ‐‐ 8E‐04 1E‐05 2E‐02 2E‐03 1E‐02 3E‐04 ‐‐ ‐‐ 6E‐03 1E‐02 ‐‐ 8E‐05 ‐‐ ‐‐ 1E‐04 ‐‐ 8E+00 3E‐03 2E‐01 1E‐02 6E‐02 3E‐03 1E‐02 2E‐01 3E‐03 6E‐03 2E‐01 1E‐04 8E‐05 1E‐04 1E‐03 6E‐05 4E‐05 8E‐04 3E‐03 1E‐02 1E‐03 3E‐03 2E‐03 6E‐03 1E‐02 7E‐03 4E‐01 1E‐02 3E‐03 2E‐04 3E‐04 2E+00 8E‐04 2E‐03 2E‐04 9E‐04 5E‐05 2E‐04 3E‐03 5E‐05 1E‐04 3E‐03 2E‐05 1E‐05 2E‐05 3E‐04 1E‐05 7E‐06 1E‐04 2E‐04 6E‐04 3E‐04 1E‐04 1E‐04 6E‐04 1E‐03 1E‐04 7E‐02 3E‐03 8E‐04 2E‐05 7E‐05 PAGE 2 OF 3 ATTACHMENT 1, TABLE 9 Summary of Hazard Quotients and Hazard Indices RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California 10 11 Hermit Thrush (0‐2 ft bgs)  Matrix Type Soil O Soil O Soil O Soil O Extrapolated Data Soil O Soil O  ERAClass Chemical of Potential Ecological Concern 12 13 Deer Mouse (0‐6 ft bgs) Terrestrial  Soil  Low  High  Low  High  Plants Invertebrates EcoRBSL  EcoRBSL  EcoRBSL  EcoRBSL  (0‐2 ft bgs) (0‐2 ft bgs) HQ HQ HQ HQ VOC VOC VOC VOC Ethylbenzene Methylene chloride Styrene Xylenes, Total ‐‐ ‐‐ 2E‐06 4E‐07 ‐‐ ‐‐ ‐‐ 6E‐06 ‐‐ ‐‐ ‐‐ 3E‐07 ‐‐ ‐‐ ‐‐ ‐‐ 8E‐06 1E‐04 2E‐06 4E‐04 8E‐07 1E‐05 1E‐06 3E‐04 PCBs PCBs PCB_TEQ_Bird PCB_TEQ_Mammal Aroclor HI Dioxin_Furan TEQ PAH‐HighMW HI PAH‐LowMW HI OC Pesticide HI ‐‐ ‐‐ ‐‐ ‐‐ 3E+01 ‐‐ 1E+00 2E+00 6E‐02 2E‐01 2E+00 3E+00 ‐‐ 2E‐01 2E‐01 ‐‐ 2E‐02 3E‐02 ‐‐ 7E+01 1E+00 3E+01 6E‐01 3E‐03 4E‐01 ‐‐ 7E+00 5E‐01 3E+00 1E‐02 5E‐04 8E‐02 Notes:  ‐‐ =  EcoRBSL was not available for receptor/chemical, chemical was not a CPEC for that receptor and/or depth interval. Chemicals in italics (Aroclor‐1248) were never detected, but were retained at CPECs in the sample quantitation limit screen. bold = HQ>1 BHC = benzene hexachloride ERA = ecological risk assessment ft = feet  HI = hazard index HQ = hazard quotient MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  MW = molecular weight PAH = polcyclic aromatic hydrocarbon PCB = polychlorinated biphenyl RBSL = risk‐based screening level SVOC = semivolatile organic compound TEQ = toxicity equivalent  VOC = volatile organic compound EN0411151012BAO  PAGE 3 OF 3 ATTACHMENT 1, TABLE 10 Hot‐spot Evaluation for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California 10x High EcoRBSL Screen    Depth  Matrix Interval  ERAClass Measured Data Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Soil 0‐6 ft Energetics Inorganics Inorganics Inorganics Inorganics Inorganics Inorganics ARCL ARCL ARCL Dioxin_Furans Dioxin_Furans Herbicides Herbicides Herbicides PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐HighMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW PAH‐LowMW Pesticides Pesticides Pesticides EN0411151012BAO  Chemical of Potential Ecological  Concern Perchlorate Antimony Arsenic Fluoride Hexavalent Chromium Nitrite‐NO2 Silver Aroclor‐1254 Aroclor‐1260 Aroclor‐5460 DioxinFuran_TEQ_Bird DioxinFuran_TEQ_Mammal 2,4‐Dichlorophenoxybutyric acid MCPA Silvex Benzo(a)anthracene Benzo(a)pyrene Benzo(b)fluoranthene Benzo(ghi)perylene Benzo(k)fluoranthene Chrysene Dibenzo(a,h)anthracene Indeno(1,2,3‐cd)pyrene Pyrene Acenaphthene Acenaphthylene Anthracene Fluoranthene Fluorene Naphthalene Phenanthrene 4,4'‐DDD 4,4'‐DDT beta‐BHC Units Minimum  Maximum  High  Detect EcoRBSL mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  0.043 7.5 110 11.2 3.2 0.82 3.5 0.099 0.046 0.00706 0.000025 0.0000519 0.032 0.94 0.0014 1.2 0.74 1 0.23 0.52 1.5 0.096 0.26 2.5 0.017 0.0021 0.13 2.3 0.015 0.0022 0.91 0.0018 0.019 0.00073 7.7 2 31 140 30 ‐‐ 29 0.39 0.25 0.39 0.000057 0.000005 19 0.61 1.8 50 310 150 460 310 76 140 300 73 11 3.3 22 880 8.9 130 13 0.85 0.58 2.9 10x High  EcoRBSL Max>10x  High  EcoRBSL Potential  Hot Spot 77 20 310 1400 300 ‐‐ 290 3.9 2.5 3.9 0.00057 0.00005 190 6.1 18 500 3100 1500 4600 3100 760 1400 3000 730 110 33 220 8800 89 1300 130 8.5 5.8 29 No No No No No ‐‐ No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No No No No No No ‐‐ No No No No No Yes No No No No No No No No No No No No No No No No No No No No No No PAGE 1 OF 2 ATTACHMENT 1, TABLE 10 Hot‐spot Evaluation for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California 10x High EcoRBSL Screen    Depth  Matrix Interval  ERAClass Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides Pesticides SVOC VOC VOC VOC VOC VOC 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft 0‐6 ft Chemical of Potential Ecological  Concern Endosulfan I Endosulfan sulfate Endrin Endrin aldehyde Heptachlor Heptachlor epoxide Mirex Di‐n‐octyl phthalate Acetone Ethylbenzene Methylene chloride Styrene Xylenes, Total Units mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  mg/kg  Minimum  Maximum  High  Detect EcoRBSL 0.00055 0.00055 0.0005 0.0011 0.00058 0.00047 0.0047 0.099 0.016 0.000312 0.00281 0.000723 0.00136 4.2 4.4 0.079 0.092 3.6 0.0065 0.34 130 230 240 230 420 4.2 10x High  EcoRBSL Max>10x  High  EcoRBSL Potential  Hot Spot 42 44 0.79 0.92 36 0.065 3.4 1300 2300 2400 2300 4200 42 No No No No No No No No No No No No No No No No No No No No No No No No No No Notes: Yes  = potential hot spot BHC = benzene hexachloride ERA = ecological risk assessment ft = feet  MCPA = 2‐methyl‐4‐chlorophenoxyacetic acid  mg/kg = milligrams per kilogram  MW = molecular weight PAH = polycyclic aromatic hydrocarbon RBSL = risk‐based screening level SVOC = semivolatile organic compound VOC = volatile organic compound EN0411151012BAO  PAGE 2 OF 2 ATTACHMENT 1, TABLE 11 Summary of Samples Used in the Radionuclide Ecological Risk Assessment  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site,  Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Location ID Soil A3_SED_DG‐11 A3_SED_DG‐12 A3_SED_DG‐13 A3_SED_DG‐14 SL‐143‐SA5C Sample ID SL‐011‐A3‐SB‐0.0‐0.5 SL‐012‐A3‐SB‐0.0‐0.5 SL‐013‐A3‐SB‐0.0‐0.5 SL‐014‐A3‐SB‐0.0‐0.5 10244 Sample Date Sample  Type Start  Depth  (ft) End  Depth  (ft) Terrestrial  Biota 05‐Oct‐11 05‐Oct‐11 05‐Oct‐11 05‐Oct‐11 20‐Oct‐10 N N N N N 0 0 0 0 0 0.5 0.5 0.5 0.5 0.5 x x x x x Notes: ‐‐ = not used ft = feet N = primary sample x = Sample results used for this exposure scenario EN0411151012BAO  PAGE 1 OF 1 ATTACHMENT 1, TABLE 12 Detected Analytes in Media of Ecological Concern RCRA Facility Investigation, Data Summary and Findings  Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Soil (0 to 2 feet bgs) Actinium‐228 Americium‐241 Americium‐243 Antimony‐125 Barium‐137m Bismuth‐212 Bismuth‐214 Cesium‐134 Cesium‐137 Curium‐243/244 Europium‐155 Lead‐212 Lead‐214 Plutonium‐239/240 Plutonium‐244 Potassium‐40 Radon‐220 Radon‐222 Strontium‐90 Tellurium‐125m Thallium‐208 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 EN0411151012BAO  PAGE 1 OF 1 ATTACHMENT 1, TABLE 13 Summary Statistics for Detected Radionuclides RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, Californi 14 15  Matrix  Depth  Interval Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft 0‐2 ft R R R R R R R R R R R R R R R R R R R R R R R R R R R R R R  EcoRAClass Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Radiochemistry Preferred Analyte Name Units Actinium‐228 Americium‐241 Americium‐243 Antimony‐125 Barium‐137m Bismuth‐212 Bismuth‐214 Cesium‐134 Cesium‐137 Curium‐243/244 Europium‐155 Lead‐212 Lead‐214 Plutonium‐239/240 Plutonium‐244 Potassium‐40 Radon‐220 Radon‐222 Strontium‐90 Tellurium‐125m Thallium‐208 Thorium‐228 Thorium‐229 Thorium‐230 Thorium‐232 Thorium‐234 Uranium‐233/234 Uranium‐235/236 Uranium‐238 Yttrium‐90 pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g pCi/g 18 19 20 Qualifier of  Depth of  Maximum  Maximum   Minimum  Maximum  Location of   Number   Number  Detected  Detected   Minimum  Maximum  SQL for  SQL for  Maximum  of  Concentratio Concentratio  Arithmetic  of   Frequency   Percent  Detected  Detected  Non‐ Non‐ Detected  Detects Analyses of Detects Detects n n Mean Value Value Value detects detects Concentration 5 4 2 2 1 5 5 1 5 2 5 5 5 2 1 5 1 1 1 1 5 5 2 5 5 5 5 5 5 1 5 5 4 5 1 5 5 5 5 5 5 5 5 5 1 5 1 1 5 1 5 5 5 5 5 5 5 5 5 4  5/5   4/5   2/4   2/5   1/1   5/5   5/5   1/5   5/5   2/5   5/5   5/5   5/5   2/5   1/1   5/5   1/1   1/1   1/5   1/1   5/5   5/5   2/5   5/5   5/5   5/5   5/5   5/5   5/5   1/4  100 80 50 40 100 100 100 20 100 40 100 100 100 40 100 100 100 100 20 100 100 100 40 100 100 100 100 100 100 25 0.993 0.00175 0.00703 0.025 0.0267 0.693 0.856 0.0109 0.0166 0.00182 0.0511 1.2 0.948 0.00409 0.0022 18.6 1.37 1 0.275 0.0276 0.364 0.761 0.0376 0.599 0.76 1.02 0.48 0.0252 0.518 0.275 1.32 0.0135 0.0129 0.119 0.0267 1.1 0.99 0.0109 0.0446 0.0128 0.089 1.64 1.06 0.00783 0.0022 20.1 1.37 1 0.275 0.0276 0.545 1.25 0.0454 0.958 1.23 1.76 0.852 0.0564 0.837 0.275  NA  0.0087 0.0215 0.0366  NA   NA   NA  0.0122  NA  0.0025  NA   NA   NA  0.0015  NA   NA   NA   NA  0.054  NA   NA   NA  0.021  NA   NA   NA   NA   NA   NA  0.177 16  NA 0.0087 0.0226 0.04  NA  NA  NA 0.058  NA 0.0209  NA  NA  NA 0.0185  NA  NA  NA  NA 0.314  NA  NA  NA 0.0962  NA  NA  NA  NA  NA  NA 0.314 17 SL‐143‐SA5C  A3_SED_DG‐13  A3_SED_DG‐12  SL‐143‐SA5C  SL‐143‐SA5C  SL‐143‐SA5C  SL‐143‐SA5C  A3_SED_DG‐11  A3_SED_DG‐14  A3_SED_DG‐11  A3_SED_DG‐13  SL‐143‐SA5C  A3_SED_DG‐14  A3_SED_DG‐13  SL‐143‐SA5C  A3_SED_DG‐14  SL‐143‐SA5C  SL‐143‐SA5C  A3_SED_DG‐14  SL‐143‐SA5C  SL‐143‐SA5C  SL‐143‐SA5C  A3_SED_DG‐14  SL‐143‐SA5C  SL‐143‐SA5C  SL‐143‐SA5C  SL‐143‐SA5C  A3_SED_DG‐13  SL‐143‐SA5C  A3_SED_DG‐14  0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5  =   =   =   J   =   =   =   J   =   =   J   =   =   =   =   =   =   =   =   J   =   =   =   =   =   =   =   =   =   =  1.11 0.00608  NA  0.0438  NA  0.842 0.897  NA  0.0327 0.00548 0.0719 1.32 0.997 0.00447  NA  19.3  NA   NA   NA   NA  0.408 1.1 0.0347 0.777 1.06 1.41 0.651 0.0429 0.662  NA  21  Standard  Deviation 0.123 0.00403  NA  0.0376  NA  0.155 0.0567  NA  0.0107 0.00518 0.0142 0.189 0.0458 0.0026  NA  0.607  NA   NA   NA   NA  0.0771 0.203 0.0102 0.145 0.189 0.27 0.134 0.0127 0.145  NA  22 23   Recommend ed UCL  Recommended UCL Basis 1.23 0.0106  NA  0.126  NA  0.99 0.951 0.0309 0.0429 0.0165 0.0854 1.5 1.04 0.009  NA  19.8  NA   NA  0.312  NA  0.482 1.29 0.0524 0.915 1.24 1.67 0.779 0.055 0.801  NA  95% Student's‐t UCL 95% KM (t) UCL Fewer Than Five Samples 95% Chebyshev UCL* Fewer Than Five Samples 95% Student's‐t UCL 95% Student's‐t UCL 95% Chebyshev UCL* 95% Student's‐t UCL 95% Chebyshev UCL* 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% KM (t) UCL Fewer Than Five Samples 95% Student's‐t UCL Fewer Than Five Samples Fewer Than Five Samples 95% Chebyshev UCL* Fewer Than Five Samples 95% Student's‐t UCL 95% Student's‐t UCL 95% KM (t) UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL Fewer Than Five Samples 24 RME EPC 1.23 0.0106 0.0129 0.119 0.0267 0.99 0.951 0.0109 0.0429 0.0128 0.0854 1.5 1.04 0.00783 0.0022 19.8 1.37 1 0.275 0.0276 0.482 1.25 0.0454 0.915 1.23 1.67 0.779 0.055 0.801 0.275 25 RME EPC Basis 95% Student's‐t UCL 95% KM (t) UCL Maximum Result Maximum Result Maximum Result 95% Student's‐t UCL 95% Student's‐t UCL Maximum Result 95% Student's‐t UCL Maximum Result 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL Maximum Result Maximum Result 95% Student's‐t UCL Maximum Result Maximum Result Maximum Result Maximum Result 95% Student's‐t UCL Maximum Result Maximum Result 95% Student's‐t UCL Maximum Result 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL 95% Student's‐t UCL Maximum Result Notes: *  ProUCL Version 5 does not offer a calculated UCL when there are too few unique detected results (one or sometimes more than one). In these cases, the 95% Chebyshev UCL using a proxy value of 1/2 the detection limit for NDs was selected as the EPC.   ft = feet  pCi/g = picocuries per gram SQL = sample quantitation limit EN0411151012BAO  PAGE 1 OF 1 Appendix E3 Identification of CMS and NFA Areas for EEL RFI Site APPENDIX E3  Identification of Corrective Measures Study and No Further Action Areas Based on Risk Assessments 1.0 Purpose The chemicals of concern (COCs) identified based on the results of the human health risk assessment  (HHRA), provided as Appendix E1, and chemicals of ecological concern (COECs) based on the ecological risk  assessment (ERA), provided as Appendix E2, serve to focus the selection of those media and areas to be  evaluated for corrective actions (referred to as corrective measures study [CMS] areas). At the RFI site scale,  this evaluation excludes groundwater to identify CMS areas for surficial media (soil and soil vapor). COCs in  groundwater that are recommended for CMS based on risk assessment are identified at the Boeing RFI  subarea scale and described further in the 5/9S Data Summary Findings Report (DSFR).  Once surficial media CMS areas are identified, the remaining areas outside the CMS areas are further  evaluated to document that residual concentrations result in incremental site risks or hazards below or near  the California Environmental Protection Agency, Department of Toxic Substances Control’s (DTSC’s) point‐ of‐departure threshold values. The results of the identification of CMS and no further action (NFA) areas  based on the Environmental Effects Laboratory (EEL) RCRA facility investigation (RFI) site risk assessments  are provided in the following subsections. CMS areas were identified to address both HHRA and ERA  potential risks and hazards using the approach outlined below.  1.1 Corrective Measure Study Areas The primary drivers to unacceptable human health risk for the hypothetical suburban resident at the EEL RFI  site, and/or those chemicals representing defined hot spots (see Section 9 or Appendix E1), have been  identified as COCs. The COCs based on the HHRA are arsenic; 2,3,7,8‐TCDD toxicity equivalents (TEQs); and  benzo(a)pyrene for soil; and trichloroethene and benzene for soil vapor. The results of the ERA, provided in  Appendix E2, identified 2,3,7,8‐TCDD TEQ as a COEC for soil (for the deer mouse). These COCs/COECs were  therefore the focus of delineation of CMS areas.  The overall objective for identification of CMS areas was to delineate the areas that, if remediated, would  result in an acceptable residual risk and hazard both to the hypothetical suburban resident and to ecological  receptors. Inherent in this evaluation is the assumption that if the areal average concentration within the  EEL RFI site (as represented by the upper confidence limit [UCL]) results in acceptable risk following a  corrective action, then the remedial objective is achieved.  The process for identifying those portions of the site to be selected as CMS areas included “removing”  sample data iteratively from the site data set until residual site incremental risk and hazard estimates  equaled or were less than DTSC’s point‐of‐departure risk threshold values or background levels, if higher.  Post‐remediation risk and hazard estimates are termed “residual” risk. For human health, the points of  departure are an incremental cancer risk of 1 x10‐6 or a hazard index (HI) of 1. For small‐home‐range  ecological receptors, the point of departure is an incremental hazard quotient (HQ) of 1 (or HI of 1, where  appropriate) at the High ecological risk‐based screening level (EcoRBSL). Samples are iteratively removed  from the human health and/or ecological risk datasets until both thresholds (or background if higher) are  achieved, to the extent feasible.    EN0411151012BAO   1 APPENDIX E3 IDENTIFICATION OF CORRECTIVE MEASURES STUDY AND NO FURTHER ACTION AREAS BASED ON RISK ASSESSMENTS In summary, the approach to identify CMS areas for surficial media based on risk assessment results  included:   Identifying preliminary CMS areas where the highest concentrations of COCs/COECs occur, with  consideration given to operational release mechanisms, migration pathways, spatial colocation of  exceedances, and natural features such as bedrock outcrops.   Calculating residual risk for the site by removing sample results within the preliminary CMS areas  from the risk assessment datasets (simulating the effect of remediating these soil areas to  acceptable concentrations)1.    Comparing residual risk and hazard estimates to DTSC’s point‐of‐departure threshold levels (or  background) for the suburban resident and small‐home‐range ecological receptors.  - If the residual risk and hazard estimates were below or near the point‐of‐departure values (or  background if higher), then the preliminary CMS areas were presented as recommended CMS  areas.  - If residual risk and/or hazard estimates exceeded the point of departure values (or background  if higher), then additional areas with sample(s) containing high concentrations of COCs/COECs  were identified for potential corrective action; those sample(s) were removed from the risk  dataset, and residual risks and hazards were recalculated.  - This step was performed iteratively until acceptable incremental risk and hazards were achieved  for the RFI site.  For the EEL RFI site COCs/COECs, target screening levels were used to determine when soil and soil vapor  CMS areas were adequately defined. These screening levels were selected as the lowest of the Suburban  Resident or Eco High RBSLs or background, if the RBSL was less than background. They served as target  concentrations to attain as an areal average (as represented by the UCL) by iteratively “removing” sample  data from the risk dataset to achieve an incremental residual risk and hazard at or near the DTSC point‐of‐ departure threshold values. The target screening levels used for the EEL RFI site COCs/COECs were:  Soil:   Arsenic: 10.84 milligrams per kilogram (mg/kg), based on the 95 percent UCL of background   2,3,7,8‐TCDD TEQ: 4.81 x 10‐6 mg/kg, based on the Suburban Resident RBSL   Benzo(a)pyrene: 3.87 x 10‐2 mg/kg, based on the Suburban Resident RBSL  Soil Vapor:   Trichloroethene: 593 micrograms per cubic meter, based on the Suburban Resident RBSL   Benzene: 83.9 micrograms per cubic meter, based on the Suburban Resident RBSL  The CMS areas delineated using this process are depicted on Figure 4‐7 of this EEL DSFR and will be  evaluated further during the CMS evaluation for the Boeing RFI subareas.  1.2 No Further Action Human Health Risk Evaluation As described above and as part of the weight‐of‐evidence documentation supporting the NFA  recommendations for the EEL RFI site, the residual human health risks and hazards were characterized for  the portions of the EEL RFI site outside of those areas recommended for CMS (presented on Figure 6‐1 of  this EEL DSFR) using the same sum‐of‐fractions approach as used for the site HHRA. The residual risk and  hazard estimates included the same COPCs as included for the initial site estimates; however, EPCs were                                                               1 If a high concentration data point was from a subsurface soil horizon, samples immediately above that sample point (if any) were also removed  from the data set, assuming shallower soil would be removed during excavation of the deeper contamination.  2 EN0411151012BAO APPENDIX E3 IDENTIFICATION OF CORRECTIVE MEASURES STUDY AND NO FURTHER ACTION AREAS BASED ON RISK ASSESSMENTS computed using the data set that excluded the CMS areas. The risk and hazard estimates provided below are  for the hypothetical suburban residential exposure scenario.   1.2.1 Direct Contact with Soil The residual excess lifetime cancer risk (ELCR) and HI estimates for the suburban resident exposure scenario,  derived using the sum‐of‐fractions approach, are summarized in Table E3‐1. The residual risk calculations for  the 0‐to‐2‐foot‐bgs (below ground surface) soil interval are provided in Table E3‐2, and the residual risk  calculations for the 0‐to‐10‐foot‐bgs soil interval are provided in Table E3‐3. The residual risk estimates for  the 0‐to‐10‐foot‐bgs interval are higher and therefore are used for computation of incremental risk. The risk  calculation table for background soil was provided as Table E1‐5 of Appendix E‐1. The chemical‐specific  incremental risks and hazards for COPCs detected in soil are provided in Table E3‐4.  For the direct soil contact pathway, the residual incremental ELCR from all carcinogenic COPCs in 0‐to‐10‐ foot‐bgs soil is 9 x 10‐7, which is below both the United States Environmental Protection Agency (USEPA)  target risk range of 1 x 10‐6 to 1 x 10‐4 and the DTSC point‐of‐departure threshold value of 1 x 10‐6 for the  areas recommended for NFA. The residual incremental HI for the NFA areas is 0.1, which is below the USEPA  and DTSC threshold HI value of 1.  1.2.2 Indoor Air Pathway The residual risk and hazard calculations for site soil vapor are provided in Table E3‐5. For the indoor air  pathway, the residual ELCR from all carcinogenic COPCs in soil vapor is 2 x 10‐8, which is below both the  USEPA target risk range of 1 x 10‐6 to 1 x 10‐4 and the DTSC point‐of‐departure threshold value of 1 x 10‐6 for  the areas recommended for NFA. The residual HI for the NFA areas is 0.0009, which is below the USEPA and  DTSC threshold HI value of 1.  1.3 No Further Action Ecological Risk Evaluation As part of the weight‐of‐evidence documentation supporting the NFA2 recommendations for the EEL RFI  site, the residual ecological risks were also characterized for the portions of the EEL RFI site outside of those  areas recommended for CMS (presented on Figure 6‐1 of this EEL DSFR) using the same sum‐of‐fraction  approach as used for the site ERA. The residual risk calculation for the single COEC identified for site soil is  provided in Table E3‐6, along with the incremental HQ.   Dioxin/furan TEQ for mammals was the only COEC identified for the EEL RFI site. The background evaluation  of the portions of the EEL RFI site outside of those areas recommended for CMS indicated that the residual  site dioxin/furan TEQs were not significantly different from background. Moreover, residual risks for these  areas were calculated, and all HQs /HIs were less than 1.   2.0 Conclusions The results from the HHRA and ERA demonstrate that acceptable risks and hazards from potential exposure  to soil and soil vapor by hypothetical suburban residents and ecological receptors are expected at the EEL  RFI site if the CMS areas presented in Figure 6‐1 of this EEL DSFR are included in site cleanup activities during  the corrective measures implementation. As described in the 5/9 South DSFR, the CMS areas identified in  this report will be further evaluated for the appropriate type of corrective action in the CMS.                                                               2 Final NFA recommendations will be confirmed following the completion of the Large‐Home‐Range ERA.  EN0411151012BAO 3 Tables List of Tables E3‐1  Residual Human Health Risk Assessment Summary  E3‐2  Residual Human Health Risk and Hazard Estimates for Exposure to Soil (0 to 2 feet bgs)  E3‐3  Residual Human Health Risk and Hazard Estimates for Exposure to Soil (0 to 10 feet bgs)  E3‐4  Chemical‐specific Incremental Risk and Hazard Estimates for Soil  E3‐5  Residual Risk and Hazard Estimates for Exposure to Soil Vapor  E3‐6  Estimated Site and Incremental Risks for Non‐CMS Areas for Chemicals of Ecological Concern  TABLE E3‐1 Residual Human Health Risk Assessment Summary RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Primary Contributors Primary Contributors to Cancer Riska to Hazard Indexa Excess Lifetime Cancer Risk Noncancer Hazard Index 2E‐06 0.2 2,3,7,8‐TCDD TEQ (ELCR=1E‐6,  None identified Background Soil Direct Contact 2E‐04 2E‐04 0.6 0.5 Arsenic (ELCR=2E‐4, 99%) Arsenic (ELCR=2E‐4, >99%) None identified None identified Incremental Risk for Soil Contactc Soil Vapor (Indoor Air Pathway) 9E‐07 2E‐08 0.1 0.0008 Exposure Scenario Suburban Residential Scenario Site Soil 0 to 2 ft bgs Direct Contact Site Soil 0 to 10 ft bgs Direct Contact b None identified None identified None identified None identified Notes: a  Primary contributors to the total risk are listed when chemical‐specific risk > 10‐6. Primary contributors to the hazard index are listed when hazard index > 1.  b  Background risk is based on data from the Final Chemical Soil Background Study Report  (DTSC, 2012). c  Incremental risk is calculated as the site risk minus the background risk. For the suburban resident, the higher risk of 0 to 2 ft bgs or 0 to 10 ft bgs is   used in the calculation. bgs = below ground surface ELCR = excess lifetime cancer risk ft = feet TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0411151012BAO PAGE 1 OF 1 TABLE E3‐2 Residual Human Health Risk and Hazard Estimates for Exposure to Soil (0 to 2 feet bgs)  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California Analyte  2,3,7,8‐TCDD TEQ  2,4‐Dichlorophenoxybutyric acid   4,4'‐DDT   Anthracene   Antimony   Aroclor 1254   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Fluoranthene   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Styrene   Xylenes, Total  Exposure Point  Carcinogeni c Concentration RBSLa (mg/kg) 4.92E‐06 4.81E‐06 3.20E‐02 1.33E‐02 1.23E‐03 3.25E‐01 5.82E‐02 2.81E‐03 2.80E‐03 4.99E‐03 3.48E‐03 7.26E‐03 2.34E‐03 5.63E‐02 5.50E‐04 7.35E‐03 4.70E‐04 1.25E+00 2.52E‐03 2.70E‐03 3.81E‐03 1.59E‐03 1.76E‐02 4.81E‐03 6.80E‐03 8.51E‐01 5.48E‐04 3.72E‐04 ‐‐ 1.74E+00 ‐‐ ‐‐ 2.32E‐01 3.87E‐01 3.87E‐02 3.87E‐01 ‐‐ 3.87E+00 1.13E‐01 ‐‐ ‐‐ ‐‐ 1.07E‐01 1.29E+00 3.87E‐01 2.97E+00 3.28E‐02 1.46E+01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Soil Contact Exposure Scenario Noncarcinogenic Percent Contributio RBSLa Cancer Hazard n Risk (mg/kg) Quotient 1.02E‐06 41.1% 5.05E‐05 9.74E‐02 ‐‐ 7.65E‐09 ‐‐ ‐‐ 2.51E‐07 7.26E‐09 7.23E‐08 1.29E‐08 ‐‐ 1.88E‐09 2.07E‐08 ‐‐ ‐‐ ‐‐ 4.37E‐09 9.66E‐07 6.51E‐09 9.08E‐10 1.16E‐07 1.09E‐10 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2E‐06 ‐‐ 0.3% ‐‐ ‐‐ 10.1% 0.3% 2.9% 0.5% ‐‐ 0.1% 0.8% ‐‐ ‐‐ ‐‐ 0.2% 38.8% 0.3% 0.0% 4.7% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100.0% 5.49E+02 3.43E+01 1.64E+04 2.64E+01 1.10E+00 ‐‐ ‐‐ ‐‐ 1.65E+03 ‐‐ ‐‐ 6.11E+02 4.12E+02 2.20E+03 8.92E‐01 2.34E+02 ‐‐ 2.90E+02 1.37E+01 6.81E+02 5.33E+01 1.64E+04 1.65E+03 2.30E+02 1.14E+04 4.28E+02 Hazard Index 5.83E‐05 3.88E‐04 7.49E‐08 1.23E‐02 5.28E‐02 ‐‐ ‐‐ ‐‐ 2.11E‐06 ‐‐ ‐‐ 9.21E‐05 1.34E‐06 3.34E‐06 5.27E‐04 5.33E‐03 ‐‐ 9.31E‐06 2.78E‐04 2.33E‐06 3.30E‐04 2.93E‐07 4.12E‐06 3.70E‐03 4.82E‐08 8.69E‐07 0.2 Percent Contributio n 56.2% 0.0% 0.2% 0.0% 7.1% 30.5% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ 0.1% 0.0% 0.0% 0.3% 3.1% ‐‐ 0.0% 0.2% 0.0% 0.2% 0.0% 0.0% 2.1% 0.0% 0.0% 100.0% Carcinogeni c RBSLa 7.51E‐09 ‐‐ 2.87E‐03 ‐‐ ‐‐ 4.88E‐04 8.05E‐04 8.09E‐05 8.05E‐04 ‐‐ 8.06E‐03 2.38E‐04 ‐‐ ‐‐ ‐‐ 1.71E‐04 1.94E‐03 8.13E‐04 1.06E‐02 5.42E‐05 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Garden Exposure Scenario Noncarcinogenic Percent Contributio RBSLa Cancer Hazard n Risk (mg/kg) Quotient 6.55E‐04 ‐‐ 4.63E‐06 ‐‐ ‐‐ 1.19E‐04 3.49E‐06 3.46E‐05 6.20E‐06 ‐‐ 9.01E‐07 9.83E‐06 ‐‐ ‐‐ ‐‐ 2.74E‐06 6.43E‐04 3.10E‐06 2.54E‐07 7.03E‐05 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 2E‐03 42.2% ‐‐ 0.3% ‐‐ ‐‐ 7.7% 0.2% 2.2% 0.4% ‐‐ 0.1% 0.6% ‐‐ ‐‐ ‐‐ 0.2% 41.4% 0.2% 0.0% 4.5% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100.0% 2.52E‐07 2.29E+00 1.80E‐01 1.01E+02 1.39E‐01 7.21E‐03 ‐‐ ‐‐ ‐‐ 1.08E+01 ‐‐ ‐‐ 3.61E+00 1.84E+00 1.40E+01 4.53E‐03 1.08E+00 ‐‐ 3.30E‐01 7.21E‐02 5.31E+00 1.58E‐02 1.01E+02 1.04E+01 1.81E+00 4.59E+01 4.96E+01 Hazard Index 1.95E+01 1.40E‐02 7.38E‐02 1.22E‐05 2.33E+00 8.07E+00 ‐‐ ‐‐ ‐‐ 3.22E‐04 ‐‐ ‐‐ 1.56E‐02 2.98E‐04 5.23E‐04 1.04E‐01 1.16E+00 ‐‐ 8.18E‐03 5.28E‐02 2.99E‐04 1.11E+00 4.77E‐05 6.54E‐04 4.71E‐01 1.19E‐05 7.50E‐06 33 Percent Contributio n 59.2% 0.0% 0.2% 0.0% 7.1% 24.5% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.3% 3.5% ‐‐ 0.0% 0.2% 0.0% 3.4% 0.0% 0.0% 1.4% 0.0% 0.0% 100.0% Carcinogeni c RBSLa 1.80E‐05 ‐‐ 5.83E+00 ‐‐ ‐‐ 5.64E‐01 9.39E‐01 9.39E‐02 9.39E‐01 ‐‐ 9.39E+00 2.75E‐01 ‐‐ ‐‐ ‐‐ 3.60E‐01 6.27E+00 9.39E‐01 3.71E+01 1.10E‐01 2.04E+02 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Total Risk Cancer Risk 2.74E‐07 ‐‐ 2.28E‐09 ‐‐ ‐‐ 1.03E‐07 2.99E‐09 2.98E‐08 5.31E‐09 ‐‐ 7.73E‐10 8.51E‐09 ‐‐ ‐‐ ‐‐ 1.30E‐09 1.99E‐07 2.68E‐09 7.28E‐11 3.46E‐08 7.79E‐12 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 7E‐07 Recreational Exposure Scenario Noncarcinogenic Percent Contributio RBSLa Hazard n (mg/kg) Quotient 41.2% ‐‐ 0.3% ‐‐ ‐‐ 15.5% 0.4% 4.5% 0.8% ‐‐ 0.1% 1.3% ‐‐ ‐‐ ‐‐ 0.2% 30.0% 0.4% 0.0% 5.2% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 100.0% 2.36E‐04 2.56E+03 1.60E+02 7.70E+04 1.23E+02 5.14E+00 ‐‐ ‐‐ ‐‐ 7.71E+03 ‐‐ ‐‐ 2.85E+03 1.92E+03 1.03E+04 4.16E+00 1.09E+03 ‐‐ 1.82E+03 6.40E+01 4.26E+03 2.49E+02 7.70E+04 7.71E+03 1.07E+03 6.49E+04 5.69E+03 Hazard Index 2.09E‐02 1.25E‐05 8.31E‐05 1.60E‐08 2.64E‐03 1.13E‐02 ‐‐ ‐‐ ‐‐ 4.51E‐07 ‐‐ ‐‐ 1.97E‐05 2.86E‐07 7.15E‐07 1.13E‐04 1.14E‐03 ‐‐ 1.49E‐06 5.95E‐05 3.73E‐07 7.08E‐05 6.25E‐08 8.82E‐07 7.93E‐04 8.44E‐09 6.54E‐08 0.04 Percent Contributio n 56.2% 0.0% 0.2% 0.0% 7.1% 30.5% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ 0.1% 0.0% 0.0% 0.3% 3.1% ‐‐ 0.0% 0.2% 0.0% 0.2% 0.0% 0.0% 2.1% 0.0% 0.0% 100.0% Notes:  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory, Ventura County California  (MWH, 2014). bgs = below ground surface mg/kg = milligrams per kilogram TEQ = 2,3,7,8‐TCDD toxicity equivalents a EN0411151012BAO PAGE 1 OF 1 TABLE E3‐3 Residual Human Health Risk and Hazard Estimates for Exposure to Soil (0 to 10 feet bgs)  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Analyte  2,3,7,8‐TCDD TEQ  2‐Methylnaphthalene   4,4'‐DDT   Acetone   Anthracene   Antimony   Aroclor 1254   Arsenic   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Ethylbenzene   Fluoranthene   Fluoride   Heptachlor   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Silvex   Styrene  EN0411151012BAO Exposure Point  Carcinogenic RBSLa Concentration (mg/kg) (mg/kg) 4.50E‐06 4.81E‐06 2.20E‐03 5.56E‐03 1.60E‐02 1.07E‐03 2.62E‐01 3.09E‐02 1.08E+01 2.35E‐03 2.16E‐03 3.49E‐03 2.48E‐03 6.74E‐03 1.96E‐03 3.26E‐02 5.50E‐04 3.12E‐04 5.19E‐03 3.21E+00 5.80E‐04 4.70E‐04 1.03E+00 2.17E‐03 2.81E‐03 2.19E‐03 1.45E‐03 1.32E‐02 3.41E‐03 4.83E‐03 4.02E‐01 1.40E‐03 5.21E‐04 ‐‐ 1.74E+00 ‐‐ ‐‐ ‐‐ 2.32E‐01 6.58E‐02 3.87E‐01 3.87E‐02 3.87E‐01 ‐‐ 3.87E+00 1.13E‐01 ‐‐ ‐‐ 2.31E+00 ‐‐ ‐‐ 1.44E‐01 1.07E‐01 1.29E+00 3.87E‐01 2.97E+00 3.28E‐02 1.46E+01 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Suburban Residential Soil Contact Exposure Scenario Noncarcinogenic Cancer Risk 9.36E‐07 Percent Contribution 0.6% ‐‐ 3.20E‐09 ‐‐ ‐‐ ‐‐ 1.33E‐07 1.64E‐04 6.07E‐09 5.58E‐08 9.02E‐09 ‐‐ 1.74E‐09 1.73E‐08 ‐‐ ‐‐ 1.35E‐10 ‐‐ ‐‐ 4.02E‐09 4.37E‐09 7.96E‐07 5.61E‐09 9.45E‐10 6.67E‐08 9.94E‐11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ ‐‐ 0.1% 98.8% 0.0% 0.0% 0.0% ‐‐ 0.0% 0.0% ‐‐ ‐‐ 0.0% ‐‐ ‐‐ 0.0% 0.0% 0.5% 0.0% 0.0% 0.0% 0.0% ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ RBSLa (mg/kg) Hazard Quotient Percent Contribution 5.05E‐05 1.62E+02 3.43E+01 6.01E+04 1.64E+04 2.64E+01 1.10E+00 2.16E+01 ‐‐ ‐‐ ‐‐ 1.65E+03 ‐‐ ‐‐ 6.11E+02 4.12E+02 2.98E+03 2.20E+03 3.04E+03 3.43E+01 8.92E‐01 2.34E+02 ‐‐ 2.90E+02 1.37E+01 6.81E+02 5.33E+01 1.64E+04 1.65E+03 2.30E+02 5.49E+02 1.14E+04 8.91E‐02 1.36E‐05 1.62E‐04 2.66E‐07 6.51E‐08 9.94E‐03 2.81E‐02 4.99E‐01 ‐‐ ‐‐ ‐‐ 1.50E‐06 ‐‐ ‐‐ 5.34E‐05 1.34E‐06 1.05E‐07 2.36E‐06 1.05E‐03 1.69E‐05 5.27E‐04 4.39E‐03 ‐‐ 9.69E‐06 1.60E‐04 2.13E‐06 2.48E‐04 2.07E‐07 2.92E‐06 1.75E‐03 2.55E‐06 4.58E‐08 14.0% 0.0% 0.0% 0.0% 0.0% 1.6% 4.4% 78.7% ‐‐ ‐‐ ‐‐ 0.0% ‐‐ ‐‐ 0.0% 0.0% 0.0% 0.0% 0.2% 0.0% 0.1% 0.7% ‐‐ 0.0% 0.0% 0.0% 0.0% 0.0% 0.0% 0.3% 0.0% 0.0% PAGE 1 OF 2 TABLE E3‐3 Residual Human Health Risk and Hazard Estimates for Exposure to Soil (0 to 10 feet bgs)  RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Analyte  Xylenes, Total  Exposure Point  Carcinogenic RBSLa Concentration (mg/kg) (mg/kg) 1.36E‐03 ‐‐ Total Risk Suburban Residential Soil Contact Exposure Scenario Noncarcinogenic Cancer Risk ‐‐ 2E‐04 Percent Contribution ‐‐ 100.0% RBSLa (mg/kg) 4.28E+02 Hazard Index Hazard Quotient 3.18E‐06 0.6 Percent Contribution 0.0% 100.0% Notes: a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory,  Ventura County California  (MWH, 2014). bgs = below ground surface mg/kg = milligrams per kilogram TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0411151012BAO PAGE 2 OF 2 TABLE E3‐4 Chemical‐specific Incremental Risk and Hazard Estimates for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Suburban Residential Soil Contact Exposure Scenario Analyte  2,3,7,8‐TCDD TEQ  2‐Methylnaphthalene   4,4'‐DDT   Acetone   Anthracene   Antimony   Aroclor 1254   Arsenic   Benzo(a)anthracene   Benzo(a)pyrene   Benzo(b)fluoranthene   Benzo(ghi)perylene   Chrysene   Dibenzo(a,h)anthracene   Di‐n‐octyl phthalate   Endosulfan I   Ethylbenzene   Fluoranthene   Fluoride   Heptachlor   Heptachlor epoxide   Hexavalent Chromium   Indeno(1,2,3‐cd)pyrene   Methylene chloride   Mirex   Naphthalene   Perchlorate   Phenanthrene   Pyrene   Silver   Silvex   Styrene  EN0411151012BAO Total Site Cancer Hazard 9.36E‐07 ‐‐ 3.20E‐09 ‐‐ ‐‐ ‐‐ 1.33E‐07 1.64E‐04 6.07E‐09 5.58E‐08 9.02E‐09 ‐‐ 1.74E‐09 1.73E‐08 ‐‐ ‐‐ 1.35E‐10 ‐‐ ‐‐ 4.02E‐09 4.37E‐09 7.96E‐07 5.61E‐09 9.45E‐10 6.67E‐08 9.94E‐11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ 8.91E‐02 1.36E‐05 1.62E‐04 2.66E‐07 6.51E‐08 9.94E‐03 2.81E‐02 4.99E‐01 ‐‐ ‐‐ ‐‐ 1.50E‐06 ‐‐ ‐‐ 5.34E‐05 1.34E‐06 1.05E‐07 2.36E‐06 1.05E‐03 1.69E‐05 5.27E‐04 4.39E‐03 ‐‐ 9.69E‐06 1.60E‐04 2.13E‐06 2.48E‐04 2.07E‐07 2.92E‐06 1.75E‐03 2.55E‐06 4.58E‐08 Background Risk Quotient 5.77E‐08 5.50E‐03 ‐‐ 4.28E‐06 1.43E‐09 7.23E‐05 ‐‐ ‐‐ ‐‐ 2.26E‐08 ‐‐ 9.71E‐03 ‐‐ ‐‐ 1.65E‐04 5.01E‐01 1.97E‐09 ‐‐ 2.19E‐08 ‐‐ 3.69E‐09 ‐‐ ‐‐ 4.56E‐07 3.02E‐10 ‐‐ 6.32E‐09 ‐‐ ‐‐ 9.88E‐06 ‐‐ 1.26E‐07 ‐‐ ‐‐ ‐‐ 5.90E‐07 ‐‐ 6.43E‐04 4.76E‐10 2.00E‐06 5.13E‐10 6.18E‐05 4.27E‐07 2.36E‐03 1.77E‐09 ‐‐ ‐‐ ‐‐ 4.14E‐09 9.91E‐06 5.91E‐11 1.26E‐06 ‐‐ 7.27E‐06 ‐‐ 5.75E‐08 ‐‐ 7.32E‐07 ‐‐ 2.26E‐04 ‐‐ ‐‐ ‐‐ ‐‐ Risk 8.78E‐07 ‐‐ 1.77E‐09 ‐‐ ‐‐ ‐‐ 1.33E‐07 ‐‐ 4.11E‐09 3.39E‐08 5.32E‐09 ‐‐ 1.44E‐09 1.10E‐08 ‐‐ ‐‐ 1.35E‐10 ‐‐ ‐‐ 3.55E‐09 3.86E‐09 3.69E‐07 3.84E‐09 9.45E‐10 6.26E‐08 4.04E‐11 ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ ‐‐ Incremental Contribution Quotient 58% 8.36E‐02 ‐‐ 9.29E‐06 0% 8.98E‐05 ‐‐ 2.66E‐07 ‐‐ 4.25E‐08 ‐‐ 2.28E‐04 9% 2.81E‐02 ‐‐ ‐‐ 0% ‐‐ 2% ‐‐ 0% ‐‐ ‐‐ 1.04E‐06 0% ‐‐ 1% ‐‐ ‐‐ 4.35E‐05 ‐‐ 1.21E‐06 0% 1.05E‐07 ‐‐ 1.77E‐06 ‐‐ 4.12E‐04 0% 1.49E‐05 0% 4.65E‐04 24% 2.03E‐03 0% ‐‐ 0% 9.69E‐06 4% 1.50E‐04 0% 8.64E‐07 ‐‐ 2.41E‐04 ‐‐ 1.50E‐07 ‐‐ 2.19E‐06 ‐‐ 1.52E‐03 ‐‐ 2.55E‐06 ‐‐ 4.58E‐08 Contribution 72% 0% 0% 0% 0% 0% 24% ‐‐ ‐‐ ‐‐ ‐‐ 0% ‐‐ ‐‐ 0% 0% 0% 0% 0% 0% 0% 2% ‐‐ 0% 0% 0% 0% 0% 0% 1% 0% 0% PAGE 1 OF 2 TABLE E3‐4 Chemical‐specific Incremental Risk and Hazard Estimates for Soil RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Suburban Residential Soil Contact Exposure Scenario Total Site Background Incremental Cancer Hazard Risk Quotient Risk Contribution Quotient Contribution Analyte  Xylenes, Total  ‐‐ 3.18E‐06 ‐‐ ‐‐ ‐‐ ‐‐ 3.18E‐06 0% Notes: a  RBSL =  risk‐based screening level from the Final Standardized Risk Assessment Methodology Revision 2 Addendum, Santa Susana Field Laboratory,  Ventura County California  (MWH, 2014). bgs = below ground surface mg/kg = milligrams per kilogram TEQ = 2,3,7,8‐TCDD toxicity equivalents EN0411151012BAO PAGE 2 OF 2 TABLE E3‐5 Residual Risk and Hazard Estimates for Exposure to Soil Vapor RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Exposure Point  Exposure Point  Concentration Concentration Analyte (µg/L) (µg/m3)  1,1,1‐Trichloroethane  1.60E‐03 1.60E+00  1,1,2‐Trichloro‐1,2,2‐trifluoroetha 2.78E‐01 2.78E+02  Chloroform  2.10E‐03 2.10E+00  Dichlorodifluoromethane  1.40E‐03 1.40E+00  Ethylbenzene  1.40E‐02 1.40E+01  Tetrachloroethene  9.50E‐03 9.50E+00  Toluene  1.29E‐01 1.29E+02  Trichlorofluoromethane  2.20E‐02 2.20E+01  Xylenes, Total  9.72E‐02 9.72E+01 c RBSLa (µg/m3) ‐‐ ‐‐ 4.59E+02 ‐‐ 9.73E+02 9.36E+03 ‐‐ ‐‐ ‐‐ Total Risk Suburban Residential Indoor Air Exposure Scenario Noncarcinogenic Percent Cancer Risk ‐‐ ‐‐ 4.58E‐09 ‐‐ 1.44E‐08 1.01E‐09 ‐‐ ‐‐ ‐‐ 2E‐08 Contributio n ‐‐ ‐‐ 22.9% ‐‐ 72.0% 5.1% ‐‐ ‐‐ ‐‐ 100.0% (µg/m3) Hazard Quotient Percent Contributio n 1.04E+06 3.13E+07 3.13E+05 1.04E+05 2.09E+06 4.17E+04 3.13E+05 7.30E+05 7.30E+05 Hazard Index 1.54E‐06 8.88E‐06 6.71E‐06 1.35E‐05 6.70E‐06 2.28E‐04 4.12E‐04 3.01E‐05 1.33E‐04 0.0008 0.2% 1.1% 0.8% 1.6% 0.8% 27.1% 49.0% 3.6% 15.8% 100.0% RBSLa Notes:  RBSL =  risk‐based screening level from the Appendix A of the Comprehensive Data Quality Objectives Report, RCRA Facility Investigation, Santa Susana Field  Laboratory, Ventura County, California  (CH2M HILL. 2013a). µg/L = micrograms per liter µg/m3 = micrograms per cubic meter a EN0411151012BAO PAGE 1 OF 1 TABLE E3‐6 Estimated Site and Incremental Risks for Non‐CMS Areas for Chemicals of Ecological Concern RCRA Facility Investigation, Data Summary and Findings Report, EEL RFI Site, Boeing RFI Subarea 5/9 South,  Santa Susana Field Laboratory, Ventura County, California Deer Mouse Risk Estimates (0‐6 ft bgs) Matrix Depth Type EcoRAClass Measured Data Sitewide COEC Soil 0‐6 ft Hazard Index DioxinFuran_TEQ_Mammal O Dioxin_Furans Dioxin_Furan TEQ Notes:  CMS = corrective measures study EcoRBSL = ecological risk based screening level EPC = exposure point concentration HQ = hazard quotient INCR = incremental nsd = not significantly different from the background population RME = reasonable maximum exposure UCL = upper concentration limit bold = HQ>1 EN0411151012BAO Backgroun Non‐CMS  RME EPC d  Evaluation (mg/kg) nsd Basis 0.00000498 99% KM (Chebyshev) UCL  Mouse  Mouse  Mouse  Non‐CMS  High  Non‐CMS  High Bkg  High  EcoRBSL HQ HQ INCR HQ 5E‐06 1E+00 1E+00 6E‐02 <1 <1 PAGE 1 OF 1 Appendix E4 Additional Data Assessment TECHNICAL MEMORANDUM   Additional Data Assessment for the Environmental Effects Laboratory RFI Site, Boeing RFI Subarea 5/9 South, Santa Susana Field Laboratory, Ventura County, California PREPARED FOR: The Boeing Company  PREPARED BY: CH2M HILL  DATE: June 3, 2015      This technical memorandum (TM) presents an assessment of additional data collected by United States  Department of Energy (DOE) at the Environmental Effects Laboratory (EEL) Resource Conservation and  Recovery Act Facility Investigation (RFI) site reporting area in Boeing RFI Subarea 5/9 South at the Santa  Susana Field Laboratory in Ventura County, California. These additional data were provided to Boeing after  preparation of the EEL Data Summary and Findings Report (DSFR) had commenced and are therefore  evaluated separately from the data presented in the DSFR. The purpose of the assessment is to determine  the potential impact (if any) the additional data have on the conclusions of human health and ecological risk  assessments presented in Section 5 and Appendices E1 through E3 of the EEL DSFR.  Eleven soil samples were collected by DOE within the EEL RFI site reporting area boundary and analyzed for  at least one of the following chemical groups: total petroleum hydrocarbons, volatile organic compounds,  semivolatile organic compounds, polychlorinated biphenyls, dioxins and furans, herbicides, metals, and  inorganics. Soil vapor samples were not collected by DOE within the EEL RFI site reporting area boundary. Of  the 11 samples collected by DOE, five are located outside of the risk‐based corrective measures study (CMS)  areas identified based on the risk assessments presented in Appendices E1 through E3 of the EEL DSFR. The  location and sample names for these five samples are listed in Table E4‐1. All five samples were collected  between 0 to 5 feet below ground surface (bgs). The locations of all 11 samples collected by DOE are  presented on Figure E4‐1.  TABLE E4‐1  Additional Samples Provided by DOE that are Outside Risk‐Based CMS Areas  Matrix  Location ID  Sample Name  Top Depth  (feet bgs)  Base Depth  (feet bgs)  Soil  A3_SED_DG‐13  SL‐013‐A3‐SB‐0.0‐0.5  0  0.5  Soil  A3_SED_DG‐14  SL‐014‐A3‐SB‐0.0‐0.5  0  0.5  Soil  5C_DG‐511  FDG‐SL‐511‐SA5C‐SB‐2.0‐3.0  2.0  3.0  Soil  5C_DG‐748  FDG‐SL‐748‐SA5C‐SB‐0.0‐0.5  0  0.5  Soil  5C_DG‐748  FDG‐SL‐748‐SA5C‐SB‐4.0‐5.0  4.0  5.0    The samples listed in Table E4‐1 are located along the drainage channel at the western end of the EEL RFI  site reporting area boundary. The existing Boeing data at the EEL RFI site in the vicinity of the sampling  results provided by DOE are sufficient to characterize chemical concentrations in soil at the site.  Concentrations above the Boeing soil characterization levels (SCLs) in the DOE samples are defined by  Boeing samples with results below SCLs. The analytical results for the samples listed in Table E4‐1 that  exceed Boeing SCLs were compared against the Boeing suburban resident risk‐based screening levels (RBSLs)  and high ecological RBSL (High EcoRBSLs), as well as 10 times the suburban resident RBSLs and 10 times the  High EcoRBSL for the most conservative ecological receptor. The results of this screening are as follows:  EN0411151012BAO 1 ADDITIONAL DATA ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE, BOEING RFI SUBAREA 5/9 SOUTH, SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CALIFORNIA  Only dioxins and furans toxicity equivalent (TEQ) for mammals in samples FDG‐SL‐511‐SA5C‐SB‐2.0‐3.0,  SL‐013‐A3‐SB‐0.0‐0.5, and SL‐014‐A3‐SB‐0.0‐0.5 exceed the suburban resident RBSLs and High EcoRBSLs.    Only dioxins and furans TEQ for mammals in sample SL‐014‐A3‐SB‐0.0‐0.5 exceeds 10 times the  suburban resident RBSL and 10 times the High EcoRBSL and may be a potential hot spot.  The data from samples listed in Table E4‐1 were combined with other data previously included in the No  Further Action residual risk evaluation (see Appendix E3) to calculate new residual risk exposure point  concentrations (EPCs) for the portions of the EEL RFI site located outside CMS areas. A comparison of these  new EPCs against the previous residual risk EPCs presented in Appendix E3 is provided in Table E4‐2 for the  0‐ to 2‐foot bgs, 0‐ to 6‐foot bgs, and 0‐ to 10‐foot bgs soil depth intervals.   TABLE E4‐2  Comparison of New Residual Risk EPC Against Previous Residual Risk EPCs 2 Previous Residual  Risk EPC (mg/kg)  New Residual Risk EPC  (Added DOE data +  Original Residual Risk  Dataset) (mg/kg)  Ratio of New  EPC to Previous  EPC  Dioxins and Furans TEQ for Mammals   4.92E‐06  1.97E‐05  4.0  0‐2  2,4‐Dichlorophenoxybutyric acid   3.20E‐02  3.20E‐02  1.0  0‐2  4,4'‐DDT   1.33E‐02  1.33E‐02  1.0  0‐2  Anthracene   1.23E‐03  1.22E‐03  1.0  0‐2  Antimony   3.25E‐01  3.22E‐01  1.0  0‐2  Aroclor 1254   5.82E‐02  6.50E‐02  1.1  0‐2  Arsenic  7.02E+00  6.91E+00  1.0  Depth  Interval (feet  bgs)  Analyte  0‐2  0‐2  Benzo(a)anthracene   2.81E‐03  2.92E‐03  1.0  0‐2  Benzo(a)pyrene   2.80E‐03  3.56E‐03  1.3  0‐2  Benzo(b)fluoranthene   4.99E‐03  5.91E‐03  1.2  0‐2  Benzo(ghi)perylene   3.48E‐03  4.10E‐03  1.2  0‐2  Chrysene   7.26E‐03  6.62E‐03  0.9  0‐2  Dibenzo(a,h)anthracene   2.34E‐03  2.26E‐03  1.0  0‐2  Di‐n‐octyl phthalate   5.63E‐02  5.45E‐02  1.0  0‐2  Endosulfan I   5.50E‐04  5.50E‐04  1.0  0‐2  Fluoranthene   7.35E‐03  7.85E‐03  1.1  0‐2  Heptachlor epoxide   4.70E‐04  4.70E‐04  1.0  0‐2  Hexavalent Chromium   1.25E+00  1.22E+00  1.0  0‐2  Indeno(1,2,3‐cd)pyrene   2.52E‐03  2.40E‐03  1.0  0‐2  Methylene chloride   2.70E‐03  2.70E‐03  1.0  0‐2  Mirex   3.81E‐03  3.81E‐03  1.0  0‐2  Naphthalene   1.59E‐03  2.34E‐03  1.5  0‐2  Perchlorate   1.76E‐02  1.44E‐02  0.8  0‐2  Phenanthrene   4.81E‐03  5.04E‐03  1.0  0‐2  Pyrene   6.80E‐03  7.06E‐03  1.0  0‐2  Silver   8.51E‐01  6.06E‐01  0.7  0‐2  Styrene   5.48E‐04  5.48E‐04  1.0  0‐2  Xylenes, Total   3.72E‐04  3.72E‐04  1.0  0‐6  Perchlorate  1.38E‐02  1.31E‐02  0.9  0‐6  Antimony  2.71E‐01  2.73E‐01  1.0  0‐6  Arsenic  1.02E+01  9.88E+00  1.0  EN0411151012BAO ADDITIONAL DATA ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE, BOEING RFI SUBAREA 5/9 SOUTH, SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CALIFORNIA TABLE E4‐2  Comparison of New Residual Risk EPC Against Previous Residual Risk EPCs Analyte  Previous Residual  Risk EPC (mg/kg)  New Residual Risk EPC  (Added DOE data +  Original Residual Risk  Dataset) (mg/kg)  Ratio of New  EPC to Previous  EPC  0‐6  Fluoride  3.15E+00  3.20E+00  1.0  0‐6  Hexavalent Chromium  1.03E+00  1.01E+00  1.0  0‐6  Silver  4.18E‐01  3.93E‐01  0.9  0‐6  Aroclor‐1254  3.25E‐02  3.89E‐02  1.2  0‐6  Dioxins and Furans TEQ for Mammals  4.98E‐06  3.00E‐05  6.0  0‐6  2,4‐Dichlorophenoxybutyric acid  2.90E‐02  3.10E‐02  1.1  Depth  Interval (feet  bgs)  0‐6  Benzo(a)anthracene  2.40E‐03  2.47E‐03  1.0  0‐6  Benzo(a)pyrene  2.21E‐03  2.69E‐03  1.2  0‐6  Benzo(b)fluoranthene  3.64E‐03  4.23E‐03  1.2  0‐6  Benzo(ghi)perylene  2.52E‐03  2.98E‐03  1.2  0‐6  Chrysene  7.17E‐03  4.84E‐03  0.7  0‐6  Dibenzo(a,h)anthracene  1.99E‐03  1.77E‐03  0.9  0‐6  Indeno(1,2,3‐cd)pyrene  2.17E‐03  2.02E‐03  0.9  0‐6  Pyrene  5.15E‐03  5.41E‐03  1.1  0‐6  Anthracene  1.08E‐03  1.12E‐03  1.0  0‐6  Fluoranthene  5.52E‐03  5.92E‐03  1.1  0‐6  Naphthalene  1.45E‐03  1.83E‐03  1.3  0‐6  Phenanthrene  3.62E‐03  4.08E‐03  1.1  0‐6  4,4'‐DDT  5.94E‐03  5.94E‐03  1.0  0‐6  Endosulfan I  5.50E‐04  5.50E‐04  1.0  0‐6  Heptachlor  5.80E‐04  5.80E‐04  1.0  0‐6  Heptachlor epoxide  4.70E‐04  4.70E‐04  1.0  0‐6  Mirex  2.27E‐03  2.27E‐03  1.0  0‐6  Di‐n‐octyl phthalate  3.44E‐02  3.26E‐02  0.9  0‐6  Methylene chloride  2.81E‐03  2.81E‐03  1.0  0‐6  Styrene  5.21E‐04  5.21E‐04  1.0  0‐6  Xylenes, Total  1.36E‐03  1.36E‐03  1.0  0‐10  Dioxins and Furans TEQ for Mammals   4.50E‐06  2.74E‐05  6.1  0‐10  2‐Methylnaphthalene   2.20E‐03  2.54E‐03  1.2  0‐10  4,4'‐DDT   5.56E‐03  5.56E‐03  1.0  0‐10  Anthracene   1.07E‐03  1.11E‐03  1.0  0‐10  Antimony   2.62E‐01  2.64E‐01  1.0  0‐10  Aroclor 1254   3.09E‐02  3.73E‐02  1.2  0‐10  Arsenic   1.08E+01  1.05E+01  1.0  0‐10  Benzo(a)anthracene   2.35E‐03  2.44E‐03  1.0  0‐10  Benzo(a)pyrene   2.16E‐03  2.64E‐03  1.2  0‐10  Benzo(b)fluoranthene   3.49E‐03  4.03E‐03  1.2  0‐10  Benzo(ghi)perylene   2.48E‐03  2.93E‐03  1.2  0‐10  Chrysene   6.74E‐03  4.78E‐03  0.7  0‐10  Dibenzo(a,h)anthracene   1.96E‐03  1.75E‐03  0.9  0‐10  Di‐n‐octyl phthalate   3.26E‐02  3.11E‐02  1.0  EN0411151012BAO 3 ADDITIONAL DATA ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE, BOEING RFI SUBAREA 5/9 SOUTH, SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CALIFORNIA TABLE E4‐2  Comparison of New Residual Risk EPC Against Previous Residual Risk EPCs Depth  Interval (feet  bgs)  Analyte  0‐10  Endosulfan I   Previous Residual  Risk EPC (mg/kg)  New Residual Risk EPC  (Added DOE data +  Original Residual Risk  Dataset) (mg/kg)  Ratio of New  EPC to Previous  EPC  5.50E‐04  5.50E‐04  1.0  0‐10  Fluoranthene   5.19E‐03  5.62E‐03  1.1  0‐10  Fluoride   3.21E+00  3.22E+00  1.0  0‐10  Heptachlor   5.80E‐04  5.80E‐04  1.0  0‐10  Heptachlor epoxide   4.70E‐04  4.70E‐04  1.0  0‐10  Hexavalent Chromium   1.03E+00  1.02E+00  1.0  0‐10  Indeno(1,2,3‐cd)pyrene   2.17E‐03  2.02E‐03  0.9  0‐10  Methylene chloride   2.81E‐03  2.81E‐03  1.0  0‐10  Mirex   2.19E‐03  2.19E‐03  1.0  0‐10  Naphthalene   1.45E‐03  1.81E‐03  1.2  0‐10  Perchlorate   1.32E‐02  1.28E‐02  1.0  0‐10  Phenanthrene   3.41E‐03  3.87E‐03  1.1  0‐10  Pyrene   4.83E‐03  5.13E‐03  1.1  0‐10  Silver   4.02E‐01  2.59E‐01  0.6  0‐10  Styrene   5.21E‐04  5.21E‐04  1.0  0‐10  Xylenes, Total   1.36E‐03  1.36E‐03  1.0        As presented in Table E4‐2, the new EPC based on the combined data set is equal to or less than the  previous EPC used for the residual risk assessments, with the following exceptions:   For the 0 to 2 feet bgs depth interval, the new EPCs for dioxins and furans TEQ for mammals, Aroclor‐ 1254, benzo(a)pyrene, benzo(b)fluoranthene, benzo(g,h,i)perylene, fluoranthene, and naphthalene  based on the combined data set are greater than the previous EPCs used for the residual risk  assessments. However, of these, only the new EPC for dioxins and furans TEQ for mammals exceeds the  suburban resident RBSL and High EcoRBSL.    For the 0 to 6 feet bgs depth interval, the new EPCs for dioxins and furans TEQ for mammals, Aroclor‐ 1254, 2,4‐dichlorophenoxybutyric acid, benzo(a)pyrene, benzo(b)fluoranthene, benzo(g,h,i)perylene,  pyrene, fluoranthene, naphthalene, and phenanthrene based on the combined data set are greater than  the previous EPCs used for the residual risk assessments. Of these, only dioxins and furans TEQ for  mammals exceeds the High EcoRBSL for burrowing mammals.   For the 0 to 10 feet bgs depth interval, the new EPCs for dioxins and furans TEQ for mammals, 2‐ methylnaphthalene, Aroclor‐1254, benzo(a)pyrene, benzo(b)fluoranthene, benzo(g,h,i)perylene,  fluoranthene, naphthalene, phenanthrene, and pyrene based on the combined data set are greater than  the previous EPCs used for the residual risk assessments. Of these, only the new EPC for dioxins and  furans TEQ for mammals exceeds the suburban resident RBSL.   Because this comparison demonstrates that the resulting residual EPC for dioxins and furans TEQ for  mammals is increased as a result of the addition of the DOE data, and because dioxins and furans TEQ for  mammals concentrations exceed the suburban resident RBSL and mammalian High EcoRBSL, a previous CMS  area for soil was expanded laterally and a new CMS area was created at a deeper depth within the extent of  an existing CMS area to include samples SL‐013‐A3‐SB‐0.0‐0.5, SL‐014‐A3‐SB‐0.0‐0.5, and FDG‐SL‐511‐SA5C‐ SB‐2.0‐3.0 at locations A3_SED_DG‐13, A3_SED_DG‐14, and 5C_DG‐511, respectively. These represent the  locations with the highest exceedances of dioxins and furans TEQ for mammals in the residual risk data set,  4 EN0411151012BAO ADDITIONAL DATA ASSESSMENT FOR THE ENVIRONMENTAL EFFECTS LABORATORY RFI SITE, BOEING RFI SUBAREA 5/9 SOUTH, SANTA SUSANA FIELD LABORATORY, VENTURA COUNTY, CALIFORNIA including sample SL‐014‐A3‐SB‐0.0‐0.5, for which the dioxins and furans TEQ for mammals concentration  exceeds 10 times the suburban resident RBSL and 10 times the High EcoRBSL. Removal of the data for these  three samples from the residual risk data set results in a residual incremental excess lifetime cancer risk and  hazard index that does not exceed the DTSC point of departure of 1 x 10‐6 and the hazard index threshold of  1 for the 0 to 2 feet bgs and 0 to 10 feet bgs depth intervals for the suburban resident, or the High EcoRBSLs  for the 0 to 2 feet or 0 to 6 feet bgs depth intervals for ecological receptors. The expanded CMS areas are  presented on Figure 6‐1 of the EEL DSFR.   The evaluation on the potential impact of additional data provided by DOE on the nature and extent of  chemicals evaluated and the human health and ecological risk assessments performed for the EEL RFI site is  considered complete on the basis of the weight‐of‐evidence evaluation presented above. An existing soil  CMS area was expanded and a new CMS area was created to include additional data; these CMS areas are  presented in Table E4‐3 (with new or revised CMS areas and their risk drivers presented in bold), on Figure  E4‐1, on Figure 6‐1, and elsewhere in the EEL DSFR. No further evaluation of human health or ecological  risks associated with the additional DOE data in the EEL RFI site reporting area is recommended during the  RFI. If needed, further evaluation of the concentrations exceeding RBSLs described in this TM will be  performed during the CMS.   TABLE E4‐3  Soil CMS Area Recommendations  CMS Area  Depth (feet)  Risk Drivers  EEL‐CMS‐S1  1  Arsenic, dioxins and furans TEQ for mammals  EEL‐CMS‐S2  2  Arsenic  EEL‐CMS‐S3  1  Arsenic  EEL‐CMS‐S4  2  Benzo(a)pyrene  EEL‐CMS‐S5  1  Dioxins and furans TEQ for mammals  EEL‐CMS‐S6  7  Dioxins and furans TEQ for mammals  EEL‐CMS‐S7  1  Dioxins and furans TEQ for mammals  EEL‐CMS‐S8  1  Dioxins and furans TEQ for mammals  EEL‐CMS‐S9  3  Dioxins and furans TEQ for mammals  New or revised CMS areas and risk drivers resulting from the evaluation presented in this TM are presented in bold.   '‐‐ = not applicable  EEL = Environmental Effects Laboratory  TEQ = toxicity equivalent    EN0411151012BAO 5 VICINITY MAP E LO P E VE D LAN D UN D NASA D ED UN DE N LA AREA I OP EL V AREA III AREA II AREA IV UNDEVELOPED LAND * EEL-CMS-S7 EEL * ** LEGEND ** * # ** * * * * * 3271 EEL-CMS-S1 * * ** * * * *** EEL-CMS-S2 * * 3227 * 3271 * * ** * 3264 * ** * EEL-CMS-S3 * 3268 * * * * * * ** *3108 * * * * * EEL-CMS-S6 * * 3109 * * 3905 * * * 3908 * * * * * SL-143-SA5C # * * # * A3_SED_DG-11 A3_SED_DG-12 ** # * EEL-CMS-S8 # EEL-CMS-S4 5C_DG-749 * A3_SED_DG-13 5C_DG-748 # # * * EEL-CMS-S5 BASEMAP LEGEND Boeing RFI Site * RFI Group Boundary Administrative Boundary EEL RFI Site Reporting Area * CUA Cluster (CC) * * Soil CMS Area Features Pipeline * Drainage Channel Operational Channel Dirt Road Paved Road 3600 Rock Outcrop Pond ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! ! * Structure Spray Field 3252 * Soil DOE Soil Former Ranch House 3251 3267 * * *** # * A3_SED_DG-14 * * * * ** ** STP-3 EEL-CMS-S9 Notes: 1) Portions of EEL RFI Site located within Administrative Area IV are being characterized by US DOE. 2) These samples were collected by DOE and evaluated separately from the data evaluated in the EEL DSFR, as presented in Appendix E4. EEL CC 1 # 5C_DG-511 * ** DRAFT Compound A Eastern Forming Pit Western Forming Pit SCO K:\BOEING\362070\MAPFILES\2015\DQO\EEL\REPORTFIGURES\EEL_FIGUREE4-1_SOILLOCS_B.MXD RANHORN 5/22/2015 10:25:44 AM $ 0 30 Feet 1 in = 60 ft FIGURE E4-1 DOE Sample Locations at the EEL RFI Site Additional Data Assessment for the Environmental Effects Laboratory RFI Site Boeing RFI Subarea 5/9 South Santa Susana Field Laboratory, Ventura County, California 60