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performed. The first will occur prior to excavati A Simco 2800H <br /> P please <br /> drill rig with a 6-inch hollow stem auger and split spoon sampler will be used <br /> to obtain samples at 1 ft, 3 ft, 5 ft and 10 ft. The second phase of sampling, <br /> to be done after the tank, fill and concrete have been removed, will allow soil <br /> samples to be taken at 6 in. to 1 ft below the excavation. Manned entry into <br /> the excavation is not expected to be necessary because a hand auger with an <br /> extension handle will be used to collect these samples. Selected samples will <br /> be analyzed for the appropriate groups of contaminants listed below, using the <br /> methods indicated: <br /> Total Extractable Fuel Hydrocarbons EPA SW846 Method 8015/3550 <br /> Ethylene Glycol and Isopropyl Alcohol EPA SW846 Method 8015/3550 modified <br /> Volatile Organics EPA SW846 Method 8240+ <br /> Semi-Volatile Organics EPA SW846 Method 8270+ <br /> Total Oil and Grease Standard Method 503D <br /> Soluble Metals CAM WET (for STLC) <br /> Those soil samples not selected for analysis will be stored in a freezer for <br /> follow-up analysis, if needed. The four borings in the gully will be filled <br /> with grout after the samples have been taken. <br /> Although the tank was tested and found to be leak tight, there may have been <br /> instances when rain runoff washed over the concrete pad underlying the drum <br /> rack. This may have possibly spread residue from the pad to soil in a <br /> localized area around the tank. Locally contaminated soil, if found, will be <br /> removed and disposed of as hazardous waste at the time of closure. Any wide <br /> spread contamination found to be present will be addressed under the Remedial <br /> Investigation/Feasibility Study at B815 and the General Services Area (Task 6 <br /> in the Site 300 Environmental Restoration Work Plan submitted to the RWQCB <br /> Central Valley Region; July 13, 1988; UCAR-10247) . <br />