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<br />       		7-Eleven Store#19976
<br />       		Quarterly Groundwater Monitoring and Remediation Progress Report(2Q2003)
<br />       		September 11, 2003
<br />       		Page 3
<br />       		maximum TPHg concentration in soil was reported at 20 feet bgs (15 4 mg/kg)   Delineation of
<br />       		hydrocarbons adsorbed to sod is considered complete at this time (Shaw, 2000)
<br />       		On September 18, 2000, as requested by the SJCPHS, 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 BTEX, TPHg, and MtBE above laboratory reporting limits   A
<br />       		grab groundwater sample was collected from boring SB-2 at a depth of 40 feet bgs  Total xylenes
<br />       		were detected at a concentration of 1 5 NgIL
<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 etches 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
<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       		x
<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 />       		perforated at 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
<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 infected 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 mg1L, after 30 minutes of sparging
<br />       		The data indicated the area of sparging influence in SP-1 includes the region of MW-2, and that
<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 infection 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
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<br />			On May 27, 2003, one sod sample was collected under the northern fuel dispenser(D14 5), and the      		�s
<br />			second sample was collected beneath the product line (1-1-4 0) during a fuel system upgrade   The     		5,1
<br />			soil samples collected beneath the dispenser and fuel delivery piping did not contain concentrations       		;
<br />			of TPHg, BTEX, or fuel oxygenates above laboratory detection limits   A soil sample was unable to
<br />			be collected from beneath the southern dispenser due to an excessive thickness of pea gravel  On      		R
<br />			June 9, 2003, three 10,000-gallon double-walled fiberglass USTs were removed from the excavation    		`se,
<br />			and hauled offsite   																,
<br />			On June 9 and 19, 2003, a total of six UST confirmation soil samples (T1N-15' through T3S-13')
<br />			were collected in native soil underlying the ends of the three USTs (Figure 2) at approximate depths
<br />			of 12 to 15 feet bgs  TPHg, BTEX, and fuel oxygenates were not detected at concentrations above
<br />			laboratory detection limits in two of the six soil samples collected beneath the USTs   Benzene and
<br />      40   	TPHg were reported in the soil samples collected beneath the north ends of two USTs (T1 N, T2N) at
<br />			19976 03-2Q Report doc     								SECOR International Incorporated
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