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1 <br /> Third Quarter 2002 Monitoring,Sampling,and Remediation Progress Report 2 <br /> 7-Eleven, Inc,Store#19976, 1399 North Main Street, Manteca,CA October 31, 2002 <br /> Underground storage tank (UST) replacement and associated soil sampling activities were conducted in <br /> September 1996 Five samples were collected at depths of 15 feet below grade (bg) from beneath the <br /> USTs Sample analysis Indicated up to 0 93 milligrams per kilogram (mg/kg) benzene, 220 mg/kg TPH-G, <br /> and 0 35 mg/kg MTBE After overexcavation, analytical results of samples collected at the edge of <br /> ' excavation were mainly non-detectable Prior to backfilling the excavation, two horizontal vent lines were <br /> installed in the northern part of the tank pit floor at a depth of 11 to 11 5 feet bg (Figure 2) The vent lines <br /> are constructed of 4-inch Schedule 40 PVC piping, each line with 20 feet of screened interval The lines <br /> ' are stubbed up inside a fiberglass box located in a planter east of the tank pit The new USTs were <br /> installed close to (partly overlapping) the location of the original USTs (Figure 2) <br /> ' A workplan for initial site assessment was requested in February 1998 by the SJCPHS Geoprobe soil <br /> borings GP-1 through GP-3 were subsequently installed on April 29, 1998, near the hydrocarbon source <br /> area (the UST pad and pump island) (Figure 2) Nineteen soil samples were collected from depths <br /> ranging between 5 and 45 feet bg for analysis for BTEX, MTBE, and TPH-G (EPA Methods 8020/modified <br /> 8015) One sample from each soil boring was also analyzed for MTBE and other oxygenates using EPA <br /> ' Method 8260 <br /> Concentrations ranged up to 15 mg/kg benzene, 2,600 mg/kg TPH-G, and 27 mg/kg MTBE (EPA Method <br /> 801518020) Highest concentrations were detected in boring GP-3 at a depth of 35 feet bg Grab <br /> groundwater samples collected from the base of each boring were also analyzed for the same <br /> constituents and contained up to 5,800 micrograms per liter (pg/L) benzene and 290,000 pg/L TPH-G <br /> Dissolved MTBE levels ranged up to 3,700 Ng/L (EPA Method 8260) (Table 1A) <br /> ' Additional assessment was requested by the SJCPHS in June 1998 Groundwater monitoring wells <br /> MW-1/1A, MW-2, and MW-3 were installed in September 1998 (Figure 2) Well MW-1/1A is a dual-nested <br /> well completed to depths of 30 and 66 feet bg Soil samples collected during well installation contained up <br /> ' to 0 07 mg/kg benzene and 0 08 mg/kg MTBE Highest concentrations were at 20 and 25 feet bg <br /> (capillary fringe soils) in wells MW-1 and MW-2 <br /> ' Soil boring SBA and nested wells MW-4/4A and MW-5/5A were installed in May 1999, as requested by <br /> the SJCPHS, to provide additional lateral and vertical plume delineation (Figure 2) Soil boring SB-1 was <br /> installed to about 65 feet bg near the UST area, to evaluate the vertical extent of the plume The nested <br /> rwells were installed to access the saturated zone at depths of 20-30 feet bg (MW-4 and M-5), and 45-50 <br /> feet bg (MW-4A and MW-5A) Soil sample data from boring SBA indicated that the base of the benzene, <br /> ' TPH-G, and MTBE/oxygenate plume lies at between 40 and 55 feet bg, as evidenced by non-detectable <br /> concentrations of all constituents Samples from well MW-5 contained low levels of gasoline constituents <br /> from 30-35 feet bg, with no detectable concentrations at deeper depths <br /> r <br /> 19976Q23 DOC <br />