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fine-grained interval is a downward-coarsening sand bed The sand is silty to fine grained in the <br /> upper part, but becomes coarse grained and gray near the base, which occurs at a depth of 32 5 feet <br /> in SW-1 and at 31 feet in VT-1 Below the sand bed is a layer of blue-gray silty clay <br /> 4.2 Soil Contamination <br /> Although VT-1 was drilled within the area that had been previously mapped as part of the soil <br /> contaminant plume, no hydrocarbon vapors or other indications of contamination were observed <br /> during drilling, and no hydrocarbons were detected by the laboratory in any of the soil samples <br /> (Table 2) Based on these results, the eastern edge of the soil plume must be moved westward, and <br /> the overall size of the plume is smaller than previously estimated <br /> Sparging well SW-1 was drilled in the approximate center of the mapped soil plume, and <br /> hydrocarbons were detected in three of the four soil samples that were collected, but at <br /> concentrations that were lower than expected Xylene was detected at the reporting limit at a depth <br /> of 20 feet, and all BTEX compounds plus TPH-g were detected at both 25 and 30 feet <br /> Concentrations increase downward to the base of the sand bed, where the coarsest, most permeable <br /> sand is present None of the gasoline oxygenates were detected in any of the samples <br /> 4.3 Depth to Groundwater <br /> The depth to groundwater has increased by about 6 inches since May (Table 1) The static water <br /> level now averages about 32 feet (16 feet below mean sea level) and is still at least 12 feet above <br /> the screened interval in the first three wells and 2 5 feet over the screen in VM-4 <br /> 4.4 Groundwater Gradient <br /> Figure 3 illustrates the groundwater gradient and general direction of groundwater flow The <br /> gradient is essentially unchanged since October 1998, and is more consistent than we have <br /> observed at most sites Flow is to the east <br /> 4.5 Groundwater Contamination <br /> Concentrations of TPH-g and BTEX in VM-1 and VM-2 have increased since the first quarter of <br /> this year, and benzene and other aromatic compounds have now appeared in VM-3 as well This <br /> is in contrast to VM-4, in which BTEX compounds have been on a decreasing trend since this <br /> well was first sampled(Table 3) None of the oxygenates were detected in any of the wells <br /> (Table 4) <br /> 5.0 SENSITIVE RECEPTOR SURVEY <br /> A sensitive receptor survey was conducted in the third quarter Upgradient personnel reviewed <br /> • the well log files of the California Department of Water Resources in Sacramento, and conducted <br /> 5 <br />