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APPENDIX BRISK BASED CORRECTIVE ACTION TIER I AND TIER 2 ANALYSIS <br /> STE CLOSURE EVALUATION REPORT <br /> Poriner Beacon Station No 695 <br /> 900 South Cherokee Lane <br /> Lodi, California <br /> Delta Project No D093-915 <br /> Page 17 <br /> SSTLs were evaluated by conservatively assuming that a drinking water well was located 250 feet directly <br /> downgradient A conservative natural attenuation factor (NAF) was estimated from site data Using the <br /> NAF, a SSTL was estimated for ground water near the source using the analysis provided in the Tier 2 <br /> Guidance Manual (Conner, et al, 1995) A SSTL was estimated for subsurface soils by using the ground <br /> water SSTL and the conservative leaching model from the Tier 2 Guidance Manual (Appendix N) <br /> 9 2 1 . Natural Attenuation Factor (NAF) <br /> Using an empirical NAF requires that the plume either exhibits a steady state or diminishing condition <br /> The NAF was determined from the March 4, 1992 data MW-1 had a concentration of 260 µg/L and <br /> MW-20 had a benzene concentration of less than 0 5 Ag/L MW-1 is located 10 feet downgradient of <br /> the source and MW-20 is located 300 feet downgradient of the source. By conservatively assuming a <br /> source concentration of 260 µg/L and a concentration of 0 5 Ag/L for the downgradient MW-20, the <br />• RBCA Tier 2 estimated a NAF of 310 <br /> 9 2 2 Ground Water SSTL <br /> By conservatively assuming that a drinking water well exists within 250 feet and using the NAF estimated <br /> in section 5 1.1, a SSTL was estimated for ground water at the source. The benzene SSTL if a drmkmg <br /> water well is installed at 250 feet from the source is 2,000 Ag/L for a residential well and 6,600 µg/L <br /> for a commercial well Using the California correction factor of 0 29 results in a SSTL of 580 tig/L <br /> The model inputs and results are summarized in Appendix O <br /> 9 2 3 Subsurface Soil SSTL <br /> The RBCA Tier 2 program utilizes a conservative leaching model to estimate the appropriate SSTL for <br /> subsurface soils that are protective of ground water receptors The model assumes equilibrium between <br /> soil and water, no benzene decay, infinite source of benzene, and conservative ground water dilution <br /> With consideration of these conservative assumptions, the subsurface soil benzene SSTL was estimated <br /> to be 23 mg/kg for a residential well and 78 mg/kg for a commercial well at 250 feet Using the <br /> RP'T001 915 <br />