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6 <br /> • 11 April 2003 <br /> AGE-NC Project No 01-0865 <br /> Page 6 of 9 <br /> Beneath the peat layer is a 30 to 40-foot fine-grained layer consisting of clay, clayey silt and silty <br /> clay,with laterally discontinuous sand layers at the top western and eastern edges of the site(Unit 2) <br /> Underlying Unit 2 is a laterally continuous sand layer(Unit 3), which comprises the deepest layer <br /> identified at the site Geologic cross sections are provided as Figures 3 and 4 <br /> Since initiation of ground water monitoring in September 1997, ground water elevations in the flat <br /> land have ranged from approximately 18 5 feet to 12 5 feet below mean sea level(MSL) The ground <br /> water elevation on the levee ranged from 3 to 5 feet above MSL (Table 3) through March 2001, <br /> when the monitoring well (MW-1) on the levee was damaged Ground water flow has consistently <br /> been east-southeast, at relatively steep gradients in the immediate area of the levee and low to very <br /> low gradients east of the existing ASTs (e g , Figure 5) <br /> i <br /> Site assessment activities to date defined two areas where soil is impacted by high concentrations <br /> of petroleum hydrocarbons The highest petroleum-hydrocarbon concentrations,up to 4,800 mg/kg <br /> TPH-g, were detected beneath the former USTs at the time of their removal Petroleum <br /> hydrocarbons, up to 4,000 mg/kg, were detected at between 5 and 10 feet bsg in pilot soil boring <br /> MW-6 approximately 5 feet west of the ASTs(Figure 2) Only the fuel additive MTBE was detected <br /> at higher concentrations at the MW-6 location <br /> Based on AGE interpretation of the available data, the initial release(s) of petroleum hydrocarbons <br /> occurred from the former USTs prior to their removal in 1991 Once released to the subsurface, the <br /> contaminants migrated through the apparently sandy levee material to a vertical depth of <br /> approximately 20 feet bsg, at which point the contaminants encountered the less permeable peat <br /> (Unit 1) and began to migrate laterally as well as vertically, lateral migration was dominantly <br /> towards the east, in the direction of ground water flow <br /> Currently, the source of the petroleum hydrocarbons impacting soil in the area of well MW-6 is <br /> equivocal The high concentrations of petroleum hydrocarbons at well MW-6, in proximity to the <br /> ASTs, may be due to a release(s) from the ASTs, a spill during fuel transfer, or because the <br /> petroleum hydrocarbons represent the down-gradient extent of the UST petroleum hydrocarbon <br /> plume The reasons for attributing a release(s)from the ASTs would be the proximity of well MW-6 <br /> to the ASTs, the high MTBE concentrations detected in the soil to greater than 15 feet bsg at well <br /> MW-6 and the high MTBE concentrations in ground water surrounding the ASTs Alternatively,the <br /> petroleum hydrocarbon impact to soil at the AST location may have originated from the USTs' <br /> release(s),which migrated within the uppermost peat layer down-gradient to the area of well MW-6, <br /> subsequent modifications to the levee and parking lot in 1997 resulted in removal of soil, including <br /> the uppermost peat,from a portion of the east side of the levee for a retaining wall According to Mr <br /> Smith, a strong odor was detected in soil removed during site modification, and several barrels of <br /> possibly contaminated soil are still stored at the site The low MTBE concentrations in the former <br /> UST area maybe an effect of the elevated location of the former USTs Meteoric waters and seepage <br /> from the Little Connection Slough,with a tidal influence,may have flushed MTBE from the shallow <br /> Advanced GeoEnvironmental,Inc <br />