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APPENDIX B: <br /> USE OF SCREENING LEVELS FOR <br /> HISTORICAL PIPELINE PORTFOLIO—BAKERSFIELD TO RICHMOND SITES <br /> The Consistent Technical Approach(CTA; Geomatrix Consultants, Inc., 2005)1 specifies use of <br /> Central Valley Regional Water Quality Control Board(RWQCB) Water Quality Objectives <br /> (WQOs) as part of the site investigation process. WQOs are defined in the Water Quality <br /> Control Plan(Basin Plan).2 The Basin Plan notes that WQOs exist in either numerical or <br /> narrative form. Where numerical limits do not exist, a numerical limit interpreting the narrative <br /> WQO is available in the State Water Resources Control Board(SWRCB) Water Quality Goals <br /> document.3 For delineation purposes at all Historical Pipeline Portfolio—Bakersfield to <br /> Richmond(HPP-BTR) sites, including the subject of this report, the WQO for each constituent is <br /> the lowest, most-conservative published numerical value. <br /> In addition to WQOs, the San Francisco Bay RWQCB Environmental Screening Levels (ESLs), <br /> which were not available at the time of CTA development, have been added as an additional <br /> screening tool for delineation decision making.4 <br /> The CTA does not prescribe the criteria by which affected soil is delineated; therefore, to achieve <br /> alignment between soil and groundwater decision making, United States Environmental <br /> Protection Agency(EPA) Regional Screening Levels (RSLs; EPA, 2008)5 and San Francisco <br /> Bay RWQCB ESLs are used to evaluate soil laboratory analytical data. <br /> In the context of a soil and groundwater investigation, RSLs, ESLs, and WQOs are screening <br /> levels used to define the extent of affected soil and groundwater, and not to assess site-specific <br /> health or ecological risks or establish cleanup standards. Further, the presence of a constituent at <br /> a concentration above a screening level does not necessarily indicate risk to human health or the <br /> environment. <br /> Total petroleum hydrocarbons (TPH) analysis and commonly fuel fingerprinting are used to <br /> distinguish HPP-BTR related petroleum hydrocarbons from other sources. The analytes at HPP- <br /> BTR sites are constituents of crude oil: TPH; benzene, toluene, ethylbenzene, and total xylenes <br /> (BTEX); and polynuclear aromatic hydrocarbons. The hydrocarbons associated with the HPP- <br /> BTR have a specific chemical profile, are typically highly weathered, and BTEX compounds are <br /> rarely present. <br /> 1. Geomatrix Consultants,Inc.,2005. Technical Approach to Site Evaluation and Decision-Making,Historical Pipeline <br /> Portfolio, Central Valley Region. February. <br /> 2. RWQCB(Central Valley Region),2008. The Water Quality Control Plan(Basin Plan)for the Sacramento River Basin and <br /> San Joaquin River Basin. Fourth Edition(revised October 2007 with approved amendments). <br /> 3. State Water Resources Control Board,2008. A Compilation of Water Quality Goals. July. <br /> 4. RWQCB(San Francisco Bay Region),2008. Screening for Environmental Concerns at Sites with Contaminated Soil and <br /> Groundwater(Interim Final). May. <br /> 5. EPA,2008. Region 9 Preliminary Remediation Goals Regional Screening Level Table. <br /> hM2://www.epa.gov/reizionO9/sLiperftmd/priz/index.html. September. <br /> B—I She Benham Companies,LLC <br /> AWholly Owned Subsidiary <br /> From Scrertce ra Sa7vlrons <br />