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' 17 May 1999 <br /> AGE-NC Project No 96-0249 <br /> Page 8 of 9 <br /> 8020 at a concentration of 18 µg11, MTBE was detected in ground water samples collected <br /> Ifrom MW-4 and MW-6 utilizing EPA Method 8260 at concentrations as high as 38 µg/1 No <br /> other fuel-oxygenate analytes were detected above laboratory reporting limits <br />' • Laboratory data indicated that the greatest concentrations of TPH-g and TPH-d in ground <br /> water are near MW-3 The distribution of known dissolved TPH-g and TPH-d are depicted <br /> in Figure 13 The horizontal and vertical extent of impacted ground water is not known <br />' • Benzene was detected in samples collected from wells MW-1 through MW-6 at <br /> concentrations exceeding the State of California Maximum Contaminant Level (MCL) for <br /> drinking water of 10 ppb The area with the highest concentrations of dissolved benzene is <br /> located near the area of MW-3 <br /> • Concentrations of toluene exceeded the MCL of 150 ,ugll at well MW-3 <br /> • Concentrations of xylenes exceeded the MCL of 1,750 ,ug/l at well MW-3 <br /> I • Grab ground water samples collected from the domestic drinking water well that services the <br /> Three B's Truck Plaza (DW-1) did not contain analyte concentrations at or exceeding <br /> laboratory reporting limits <br /> 5 0. RECOMMENDATIONS <br /> Based upon data collected during March and April 1999, AGE recommends <br /> • Further assessment of petroleum hydrocarbon-impacted soil and ground water utilizing <br /> Geoprobe soil borings, recommended soil boring locations are depicted in Figure 2 Data <br /> derived from additional hydropunch soil borings will provide a more efficient and cost <br /> effective approach for determining the number and locations of additional monitoring <br /> well(s) <br /> • Installation of additional ground water monitoring wells southwest,west,north and northeast <br /> of the foriner UST area(based on results of the Geoprobe soil bonngs) in order to assess and <br /> monitor the horizontal extent of off-site dissolved petroleum hydrocarbons (See Figure 2) <br /> Consideration should be given towards dual-completing additional ground water monitoring <br /> wells to assess hydrocarbon-impacted ground water at deeper levels <br /> I • Installation of at least one deeply screened ground water monitoring well near the former <br /> UST area to assess and monitor the extent of vertical hydrocarbon-impact <br /> • Analysis of permeability, porosity, density, moisture content and total organic content by a <br /> Geotechnical Testing Laboratory during the next phase of soil sample collection The results <br /> Advanced GcoEnvironinentai,Inc <br />