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Appendix A Site Closure Request July 2,2010 <br /> Speedy Foods-Stockton Page 10 of 13 <br /> 16.0 Discussion of Risk Assessment Model <br /> 16.1 Soil Screening Levels <br /> Vadose zone results collected from the upper 65 feet of confirmation borings CB 1 and CB2 indicate <br /> TPHg, benzene, and MTBE concentrations are below the 'Tref Environmental Screening Levels <br /> (ESLs) for residential land use (Table C-1) published by the San Francisco Bay RWQCB in the <br /> document Screening for Environmental Concerns at Sites with Contaminated Soil and Groundwater <br /> (revised May 2008). The chemicals of concern are not found in soil concentrations that would pose a <br /> risk to human—Fiea-ltli or the environment. <br /> • Final residential screening levels for TPHg in deep soil where groundwater is a potential source of <br /> drinking water is 83 milligrams per kilogram (mg/Kg). Samples collected in the upper 65 feet of <br /> CB 1 and CB2 (vadose zone) indicated that TPHg was below laboratory detection limits of 1 <br /> mg/Kg. <br /> • Final residential screening levels for benzene in deep soil where groundwater is a potential source <br /> of drinking water is 0.044 mg/Kg. Samples collected in the upper 65 feet of CBI and CB2(vadose <br /> zone) indicated that benzene was below laboratory detection limits of 0.005 mg/Kg. <br /> • Final residential screening levels for MTBE in deep soil where groundwater is a potential source of <br /> drinking water is 0.023 mg/Kg. Samples collected in the upper 65 feet of CB1 and CB2 (vadose <br /> zone)indicated that MTBE was below laboratory detection limits of 0.005 mg/Kg. <br /> 16.2 Groundwater Vapor Emissions to Indoor Air–TPHg <br /> After calibrating the ESL models for benzene and MTBE,Grotuid Zero ran models for TPHg using the <br /> physical-chemical and toxicity values in Table J of the San Francisco Bay RWQCB's Screening for <br /> Environmental Concerns at Sites with Contaminated Soil and Groundwater (revised May 2008). <br /> There were significant variations in the literature regarding normal boiling point, critical temperature, <br /> and enthalpy of vaporization. The upper and lower ends of the variables were run and the most <br /> conservative model indicated that a TPHg concentration 32,000 gg/L would generate a Tier I hazard <br /> quotient of 0.2. This conservative model does not include the adjustment upward of by a factor of 10 <br /> as recommended in Section 2.4.2.2 of Appendix 1 of the San Francisco Bay RWQCB's Screening for <br /> Environmental Concerns at Sites with Contaminated Soil and Groundwater (February 2005). The <br /> model assumes groundwater is 10 feet below ground surface. The groundwater table at the Site <br /> fluctuates between 56 and 76 feet bgs. <br /> TPHg concentrations are below the calculated Tier I ESL for TPHg at the Site. TPHg concentrations <br /> ranged between 13,000 µg/L and-1 5,000 µg/L during the last two semi-annual groundwater monitoring <br /> events. <br /> Johnson and Ettinger models showing the variations in the assessment of TPHg vapor emissions from <br /> groundwater as well as calibration models for benzene and MTBE are included in Attachment D. <br />