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S E C 0 R alternative for this site (SECOR, Dual Phase Extraction Summary Report, February 2002) On April 23, 2002, the SJCEHD expressed concern with high concentrations of tertiary butyl alcohol (TBA) in wells MW-3 and MW-7 On May 9, 2002, GRI confirmed the presence of elevated concentrations of TBA in the wells (over 200,000 pg/L), and ` attributed the raised concentrations to MtBE metabolism In correspondence dated July 22, 2002, the SJCEHD required that the groundwater samples from wells MW-3 and MW-7 be analyzed for the full scan of analytes by Environmental Protection Agency T� (EPA) Method 8260 According to the SJCEHD, other degradation constituents are ` likely present if MtBE metabolism is occurring In the areas of wells MW-3 and MW-7 ; GRI began sampling MW-3 and MW-7 for the full scan of analytes by EPA Method 8260 > during the first quarter 2003 4 In December 2002, GRI oversaw the installation of groundwater monitoring wells MW-12 and MW-13, the installation of 10 sparge points (SP-A through SP-H, SP-J, and SP-K) completed at a depth of 30 feet bgs, and drilled two additional CPT probes (CPT-2 and CPT-3) to a maximum depth of 140 feet bgs TPHg and benzene, toluene, ethylbenzene, and xylene (BTEX) constituents were not detected above laboratory method reporting limits (MRLs) in the CPT groundwater samples MtBE and methanol were detected in the 75-foot groundwater sample from CPT-2 at concentrations of 2 0 and 2,700 ppb, respectively MtBE was detected in the 100-foot groundwater sample from CPT-3 at a concentration of 6 8 ppb MtBE and TBA were detected in the 125-foot sample from CPT-3 at concentrations of 290 and 88 ppb, respectively (GRI, Groundwater Monitoring Well, CPT, and Ozone Microsparge System Installation Report, f May 2003) F� 3� An ozone sparge (OS) system was installed, connected to the sparge wells, and was brought on-line on December 20, 2002 by GRI Operation of the OS system is currently ongoing, and consists of a K-V Associates (KVA) "C-Sparge" ozone microsparging system that cycles a mixture of ozone and air into each sparge point for five to 15-minute periods, approximately 16 times per day (GRI, Groundwater Monitonng Well, CPT, and Ozone Microsparge System Installation Report, May 2003) Groundwater from the site wells has been monitored and sampled since 1990 ' tw SENSITIVE RECEPTORS A water supply well survey was performed in 1989 Results indicated the presence of one private water supply well located approximately 900 feet from the site (direction unknown), and one public water supply well located 1,'100 feet northwest of the site In April 2001, GRI conducted a well search and sensitive receptor survey (SRS) within a '/2-mile radius of the site Based on the available data supplied by the California `s Department of Water Resources (DWR), three municipal wells were identified within the � '/-mile radius of the site The closest well was located approximately 1,000 feet north- northwest of the site A 500-foot radius, door-to-door SRS was also conducted, which involved the distribution of questionnaires to residences and businesses within the site ,T t area None of the returned questionnaires indicated the presence of a water supply well within 500 feet of the site (GRI, Monitoring Well Installation Report, September 26, 11ConocoPhi1hps\Retail Sites1111921QSSR1200512Q2005 QSSR and QRPS doc U A a