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Analysis of the eight soil samples collected from the sidewall of the excavation detected <br /> petroleum hydrocarbons and BTEX constituents in three of the samples at concentrations of up <br /> to 53 mg/kg TPH in the gasoline range, 67 mg/kg TPH-D,440 mg/kg TPH-MO, and 0.065 <br /> mg/kg ethylbenzene. Analysis of the composite of the stockpiled soil samples detected up to <br /> 12 mg/kg TPH-G, 510 mg/kg TPH-MO, and 0.006 mg/kg toluene. Based on the results of the <br /> laboratory analysis, the stockpiled soil was used as backfill in the excavation. <br /> A work plan for additional soil and groundwater sampling was prepared in February 2002 at <br /> the request of PG&E to assess the extent of residual petroleum hydrocarbons and BTEX <br /> constituents in soil as well as dissolved-phase hydrocarbons in the groundwater,if any. <br /> 2.0 FIELD PROCEDURES <br /> After receipt of regulatory approval of the work plan and before performing field activities, a <br /> drilling permit was obtained from the San Joaquin County Environmental Health Department <br /> (SJCEHD). A copy of the permit is included in Appendix A. <br /> 2.1 Soil Boring <br /> On June 27 and 28,2002,seven soil borings, SB-7 through SB-13,were drilled to depths of <br /> approximately 14 feet using 4-inch-diameter hand augers at the locations shown on Figure 3. <br /> To prevent cross-contamination, all drilling equipment that may be in contact with potentially <br /> contaminated material was washed using a phosphate-free detergent followed by tap water and <br /> deionized water rinses between each use. Decontamination fluids were transferred into a tank <br /> truck for disposal at an appropriate disposal/recycling facility. <br /> Soil samples were collected using hand sampler lined with stainless steel tubes at three, six,and <br /> nine feet below grade,except in Boring SB-13,which was drilled at the location of the former <br /> excavation. As such,no soil sample of the backfill material was collected at 3 feet below grade <br /> in Boring SB-13. A slide hammer was used to advance the sampler to approximately six inches <br /> into the undisturbed soil. Soil sampling was performed following the procedures described in <br /> Appendix B and the soil samples were described in general accordance with the Unified Soils <br /> Classification System,including color,moisture, density and consistency. The soil boring logs <br /> prepared for SB-7 through SB-13 are included in Appendix C. <br /> After retrieval from the boring, the sampler was opened,the sample tubes were removed,and a <br /> soil sample was selected for chemical analysis. The sample was retained within the stainless <br /> steel tube, and both ends were immediately covered with Teflon sheeting and polyurethane <br /> caps. The caps were sealed with tape and labeled with the following information: Alisto's <br /> project number,boring number,sample depth interval,sampler's initials, and date of collection. <br /> The sample was immediately placed in a waterproof plastic bag and stored in a cooler <br /> maintained at 4oF. Possession of the samples was documented from the field to a state-certified <br /> analytical laboratory by using a chain of custody form. <br /> 2.2 Temporary Well Installation <br /> Soil Borings SB-7 through SB-13 were converted into temporary wells in accordance with the <br /> procedures described in Appendix B. During drilling and soil sampling, groundwater was <br /> encountered in each boring at approximately 10 feet below grade. After collection of soil <br /> f.\02\U1211\211-15\reportdoc <br /> 2 NINO <br />