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1 <br /> Fourth Quarter 2002 Monitoring and Sampling Report 2 <br /> 7-Eleven, Inc Store No 17334,4501 North Pershing Avenue,Stockton,CA January 13, 2003 <br />' Groundwater monitoring and sampling has been ongoing at the Exxon site since 1987, and conducted at the <br /> Cardlock and Shell sites since 1992 In 1988 Exxon installed well MW-9 to 30 feet below grade (bg), <br /> approximately 10 feet east and 10 feet south of the 7-Eleven UST area Depth to groundwater in well MW-9 <br />' has ranged from 30 feet bg in 1990 to 20 feet bg in April 1996 <br /> On February 20, 1997, Fluor Daniel GTI supervised the advancement of four angled and three vertical <br />' geoprobe borings (GP-1 through GP-7) at the site (Fluor Daniel GTI, 1997) Soil samples were collected from <br /> the borings at depths of 15 to 22 feet bg Six borings (GP-1 through GP-6)were drilled beneath the three <br />' 10,000-gallon USTs at the site as required by the SJCPHS prior to tank lining permit approval In addition, <br /> grab groundwater samples were collected from borings GP-3, GP-4, and GP-7 Benzene was detected in soil <br /> sample GP-4 @ 17 feet at a concentration of 0 0095 milligrams per kilogram (mg/kg) TPH-G was not <br />' detected in any of the soil samples collected The highest MTBE concentration was reported in sample <br /> GP-1 @ 15 feet at 0 91 mg/kg (EPA Method 8260) The highest dissolved benzene, TPH-G, and MTBE <br /> concentrations in groundwater were reported in sample GP-4 at 9,100 micrograms per liter(µg/L), <br /> 150,000 pg1L, and 84,000 µg/L, respectively <br />' Based on these data, the SJCPHS required additional assessment of soil and groundwater conditions <br /> beneath the site From September 23 through November 26, 1997, Fluor Daniel GTI supervised the drilling of <br /> five groundwater monitoring wells (MW-1, MW-1A, MW-2, MW-3, and MW-4) to depths ranging between 35 <br /> and 40 feet bg (Figure 2) Soil samples were collected during drilling at 5-foot-depth intervals from 5 feet bg <br /> to total depth In addition, soil from wells MW-1 and MW-2 was sampled continuously from 15 feet bg to total <br /> depth A total of twenty-three soil samples collected from the soil borings were submitted for laboratory <br />' analysis The groundwater monitoring wells are constructed of 2-Inch-diameter Schedule 40 poly-vinyl- <br /> chloride (PVC) casing with flush threads and 0 020-inch-slot well screen Wells MW-1, MW-2, MW-3, and <br /> MW-4 are screened from 13 to 33 feet bg, and well MW-1A is screened from 38 to 40 feet bg <br />' On August 14 1998 monitoring wells MW-1 and MWAA were abandoned, as they were located adjacent to <br />' the USTs that were removed on August 25, 1998 On August 25, 1998, approximately 200 cubic yards of soil <br /> were excavated from the new UST location to accommodate the installation of two double-wall steel 10,000- <br /> gallon USTs Samples were collected at depths of up to 14 feet bg below/adjacent to the former locations of <br />' the tanks/islands and lines (Fluor Daniel GTI, 1998) <br /> On December 17, 1998, double-nested groundwater monitoring well MW-5 (replacing abandoned well MW-11) <br />' was installed to 40 feet bg (Figure 2) Each well segment is constructed of two 2-inch diameter Schedule 40 <br /> PVC casings with flush threads and 0 020-inch-slot well screen The deep segment (MW-5B) is screened <br /> from 38 to 40 feet bg The shallow segment (MW-5A) is screened from 13 to 33 feet bg <br /> i <br /> i <br />' 173341124 QMR 110C <br />