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LFR Levine-Fricke <br /> 2.0 PRELIMINARY RI/FS <br /> The U.S. EPA Emergency Response Section, under the authority of the <br /> Comprehensive Environmental Response, Compensation and Liability Act(CERCLA) <br /> and Superfund Amendment and Reauthorization Act(SARA), directed their contractor, <br /> the Superfund Technical Assessment Response Team(START), to conduct a <br /> preliminary RI/FS of the Site. Field sampling activities were conducted from October <br /> 15 through December 13, 2001. The purpose of the preliminary RI/FS was to <br /> determine the impact on soil and groundwater quality at the Site due to the tire fire. <br /> Additionally, analytical data was gathered to determine the extent of contamination at <br /> the Site and to characterize waste for removal by the CIWMB. The preliminary R1/FS <br /> data is summarized in the "Tracy Tire Fire Site Removal Assessment Report" prepared <br /> by EEI and dated October 2002 (EEI 2002). <br /> 2.1 Soil <br /> The preliminary RI/FS included the collection of 36 soil samples from the Site during <br /> October 15 through 18, 2001, under the guidance of the U.S. Environmental Protection <br /> Agency (U.S. EPA). Figure 3 shows the locations of ten borings, four surface <br /> sampling locations, and two background sampling locations that were advanced during <br /> the preliminary RI/FS. <br /> Based on data collected during October 2001, it appears that surface soil was adversely <br /> affected by the tire fire. The impact to soil appears to be limited to those areas where <br /> tires burned. The burned areas contain elevated concentrations of metals(primarily <br /> zinc) and some areas of pyrolytic oil derived from melting tires. <br /> Soil samples were collected at the ground surface, at 6 to 8 feet below ground surface <br /> (bgs), and at 14 to 16 feet bgs from each of the 10 boring locations. Soil samples were <br /> analyzed for metals by EPA Method 6010, for volatile organic compounds (VOCs)by <br /> EPA Method 8260/5035, for semi-volatile organic compounds (SVOCs)by EPA <br /> Method 8270, and for total recoverable petroleum hydrocarbons (TRPH)by EPA <br /> Method 9071B. Five of the soil samples were analyzed for dioxins by EPA Method <br /> 8290. Tables summarizing the data are included in Appendix E. Surface soil samples <br /> were also collected in the southeastern and southwestern corners of the property to <br /> assess the site background concentrations. Regional background concentrations are <br /> provided in Appendix E from a sample located 5 miles west of the Site. <br /> Comparison of the analytical data with regional background concentrations indicate that <br /> concentrations of antimony, arsenic, cadmium, cobalt, copper, iron, lead, manganese, <br /> and zinc in surface soil samples exceeded regional background concentrations. A few <br /> of the deeper samples (6 to 8 feet and 14 to 16 feet bgs) collected exceeded the regional <br /> background arsenic concentration,but not the site background concentration for <br /> arsenic. <br /> Final_RAP_Tracy_9.18.03(final).doc Page 3 <br />