Laserfiche WebLink
S E C 0 R <br /> 7-Eleven Store#19976 <br /> Quarterly Groundwater Monitoring and Remediation Progress Report (3Q2003) <br /> . November 26, 2003 <br /> Page 3 <br /> Soil boring SB-1 and nested wells MW-4/4A and MW-5/5A were installed 3n May 1999, as requested <br /> by the SJCPHS, to provide additional lateral and vertical plume delineation Soil boring SB-1 was <br /> advanced to 65 feet bgs near the UST area, to evaluate the vertical extent of the plume The nested <br /> wells were installed to access the saturated zone at depths of 20-30 feet bgs (MW-4 and MW-5), and <br /> 45-50 feet bgs (MW4A and MW-5A) Sod sample data from boring SB-1 indicated that the base of <br /> the benzene, TPHg, and MtBE/oxygenate plume lies at between 40 and 55 feet bgs, as evidenced <br /> by non-detectable concentrations of all constituents Samples from well MW-5 contained low <br /> concentrations of gasoline constituents from 30-35 feet bgs, with no detectable concentrations at <br /> deeper depths (Shaw, 1999) <br /> Well MW-6 was installed in December 1999, to a depth of 30 feet bgs (Figure 2) Benzene and <br /> MtBE were not detected above laboratory reporting limits in the soil samples collected The <br /> maximum TPHg concentration in sod was reported at 20 feet bgs (15 4 mg/kg) Delineation of <br /> hydrocarbons adsorbed to soil is considered complete at this time (Shaw, 2000) <br /> On September 18, 2000, as requested by the SJCEHD, eleven soil-gas survey points were pushed <br /> to 3 feet bgs Significantly elevated MtBE concentrations (2,200 pg/L) were detected in only one of <br /> the points (SG-9), located along the western edge of the UST pit about 20 feet south of MW-2 <br /> On November 1, 2000, monitoring well MW-7 was installed to a depth of 30 feet bgs and soil boring <br /> SB-2 was drilled to a depth of 50 feet bgs (Figure 2) Soil samples analyzed from both well MW-7 <br /> and soil boring SB-2 did not contain benzene, toluene, ethylbenzene, xylene (BTEX), TPHg, and <br /> MtBE above laboratory reporting limits A grab groundwater sample was collected from boring SB-2 <br /> at a depth of 40 feet bgs The water sample contained total xylenes at a concentration of 1 5 fag/L t, <br /> z <br /> SVE testing conducted in 2001 using the two horizontal vent wells installed in the former UST tank <br /> pit (IT Corporation, September 2001) indicated extracted vapor concentrations of over 10,000 parts <br /> per million by volume (ppmv) at applied vacuums ranging between 9 and 32 inches of water <br /> Induced vacuum responses of more than 0 2 inches of water were observed in wells MW-1, MW-2, <br /> and MW-3 during extraction from the horizontal wells Vacuum response in these wells is likely <br /> facilitated by relatively higher-permeability conditions in the tank cavity backfill as opposed to native ,i <br /> soils Testing was also conducted on the groundwater monitoring wells, lower permeability and <br /> limited screen above the water table likely account for low extraction rates/low induced vacuum <br /> responses observed during extraction from the wells Extracted vapor concentrations ranged up to <br /> 0 91 ppmv benzene, 220 ppmv MtBE, and 880 ppmv TPHg The data indicated that vapor extraction <br /> is a viable remediation method at the site, particularly when the horizontal wells are used <br /> Double-nested sparge well SP-1 was installed on October 29-30, 2001 to a depth of 50 feet bgs and <br /> screened from 30-35 and 45-50 feet On February 6, 2002, an air sparge test was conducted using <br /> well MW-2 for vapor extraction, and double-nested sparge well SP-1 for air injection Pre-sparging 3 <br /> extracted vapor levels ranged up 1,000 ppmv, with dissolved oxygen (DO) levels of up to 0 72 mg/L <br /> Air was then injected into the deeper section of well SP-1 using an oil-less air compressor Vapor <br /> levels in well MW-2 increased to 1,600 ppmv, and DO levels to 8 mg/L, after 30 minutes of spargmg " <br /> The data indicated the area of sparging influence in SP-1 includes the region of MW-2, and thatl <br /> treatment using well SP-1 should be successful at reducing dissolved hydrocarbons/oxygenates in <br /> well MW-2 and the surrounding area Air sparge testing was repeated on May 23, 2002, using well <br /> MW-1A as the injection point and the horizontal wells as the SVE point Results indicated no <br /> breakthrough of sparged air into the vadose zone accessible by the horizontal wells <br /> ii <br /> 19976 03-3Q Report doc SECOR International Incorporated <br />