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Lead was not detected in any of the wells, and samples from KF-4, KF-6, and KF-7 continue to be <br /> below reporting limits for all hydrocarbons. Except for xylene, concentrations also remained below <br /> the reporting limits in KF-1. In KF-2, MTBE, xylene, and TBA concentrations rose slightly, and <br /> these as well as gasoline and benzene rose in KF-3 and KF-5. Hence, the concentration of most <br /> hydrocarbons increased slightly in at least three wells this quarter. <br /> 4.3 Hydrocarbon Plume Maps <br /> The contour maps that were included in the First Quarter 2002 Report were based on February data <br /> from both the Kwikee and Chevron sites, and illustrated a dissolved-phase gasoline plume that was <br /> centered near MW-1 at the Chevron site. The plume extended eastward to the beyond KF-5 at the <br /> Kwikee site but only MTBE extended eastward far enough to reach KF-2. A decreasing <br /> concentration gradient from west to east was clearly evident, reflecting the fact that concentrations <br /> beneath the Chevron site are two orders of magnitude (100 times) greater than those beneath the <br /> Kwikee site. <br /> This eastward concentration gradient is still evident in the contour maps for May 2002 (Figures 4- <br /> 6), although the plume cannot be fully mapped because Upgradient Environmental was unable to <br /> obtain the May 2002 laboratory data from Gettler-Ryan for the Chevron site. Several messages <br /> requesting the data were not returned. Hence, these maps are based only on the data from the <br /> Kwikee monitoring wells. Increases in concentrations in KF-3 and KF-5, as well as the detection of <br /> xylene and an increase in the MTBE concentration in KF-2, imply that the plume has shifted <br /> eastward slightly since February. This shift occurred while the remediation system at the Chevron <br /> site was inoperative and the groundwater flow direction reverted to its natural eastward direction, <br /> and is a further confirmation that dissolved hydrocarbons migrate eastward from the Chevron site in <br /> the absence of measures at that site to counteract normal groundwater flow. When the remediation <br /> system was in operation during the first quarter of 2002, concentrations at the Kwikee site were <br /> diluted by uncontaminated water that was drawn in from farther east. <br /> 5.0 CONCLUSIONS AND RECOMMENDATIONS <br /> The data collected during the second quarter of 2002 reveal that the water table in the immediate <br /> vicinity will rebound when no remedial activity is taking place at the Chevron site, and groundwater <br /> will return to its natural eastward flow direction. This process does not occur overnight, and water <br /> depth measurements in May indicate that the water table has equilibrated below the Kwikee Foods <br /> site but not beneath the Chevron site. As a result, groundwater continued to flow westward west of <br /> the Kwikee site, but began flowing eastward beneath the site. In response, hydrocarbon <br /> concentrations beneath the Kwikee site began increasing'again as the higher concentrations that are <br /> present beneath Franklin Street began migrating eastward. The increase in concentrations in KF-3 <br /> contradicts the January 2002 suggestion by PHS/EHD that higher soil concentrations may exist east <br /> of that well near the former UST cavity, causing concentrations to increase when groundwater <br /> flows to the west from the excavation toward KF-3. <br /> 5 <br />