Laserfiche WebLink
Report on Additional Site Assessment and Soil Vapor Extraction Testing 4 <br /> 7-Eleven Store No 20632 4627 Da Vinci Drive Stockton,CA August 14 2002 <br /> 42 Results of Sod Sample Analyses <br /> Table 1 summarizes the laboratory analytical results for soli samples collected on April 8 and 9, 2002 <br /> Benzene and TPH-G were detected above reporting limits in only one soil sample (SPV-1 @ 10') at a <br /> concentration of 0 035 mglkg and 13 mg/kg, respectively MTBE was detected in nine soil samples <br /> (Table 1), with the highest concentration in sample MW-7 @ 15 feet at 2 4 mg/kg TBA was detected in <br /> five soil samples (Table 1)with the highest concentration in sample SPV-1 @ 15 ft at 50 mg/kg TBA <br /> detections may indicate ongoing intrinsic biodegradation, as TBA is a degradation product of MTBE <br /> Other than MTBE and TBA, no oxygenates were detected above reporting limits in the soil samples <br /> analyzed Copies of the analytical results and chain-of-custody documents are included in Appendix B <br /> 43 Results of Groundwater Sample Analyses <br /> Table 1 summarizes the laboratory analytical results for Hydropunch groundwater samples collected from <br /> boring SB-1 on April 8, 2002 Benzene and TPH-G were not detected above reporting limits in either of <br /> the samples Dissolved MTBE was detected in both samples SB-1 @ 30 ft and SB-1 @ 40 ft at <br /> concentrations of 4,300 µg/L and 5,700 µg/L, respectively TBA was detected in one of the groundwater <br /> samples (SB-1 @ 30 feet) at 2,800 µg/L TBA detections may indicate intrinsic biodegradation, as TBA is <br /> a degradation product of MTBE Other than MTBE and TBA, no oxygenates were detected above <br /> reporting limits in the samples analyzed Copies of the analytical results and chain-of-custody documents <br /> are included in Appendix B <br /> so SVE EVALUATION <br /> aOn April 22, 2002, a brief SVE evaluation was conducted at the site, to determine the radius of vapor <br /> Y <br /> extraction <br /> influence and evaluate h drocarbon/oxygenate vapor production (based on field instrument <br /> data) within the vadose zone <br /> Applying vacuums of up to 50 inches of water column (IWC) using a 250-cubic-feet-per-minute (cfm) <br /> mobile (trailer-mounted) thermal oxidizer, wells MW-4R, MW-7, and SPV-2 were tested briefly <br /> (approximately 1 hour each), followed by completion of a 3 5-hour test on well SPV-1 (Appendix Q <br /> Prior to initiating the test, sampling ports on wells MW-1, MW-2, and test wells not undergoing extraction <br /> were connected to calibrated magnehelic gauges to monitor pressure changes <br /> Extracted fiowrates from SPV-1 measured during the test ranged up to 62 cfm, with extracted vapor <br /> concentrations (measured using field instruments) ranging up to 95 parts per million by volume (ppm[vl) <br /> The proximity of well SPV-1 to the UST pit (and expected communication with UST backfill gravel) did not <br /> result in higher flow rates from this well Air sparging into the AS segment of the test well did not increase <br /> concentrations in the vadose zone (although dissolved oxygen levels increased from less than 0 5 <br /> milligrams per liter[mg/Ll to 2 4 mg/L) Based on vacuum responses of up to 0 02 lWC in the nearest <br /> observation wells (located 28 feet from the extraction point), the radius of vapor extraction influence is <br /> estimated at 10 feet (Figure 2) (Table 3) <br /> 20632sardoc <br />