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March 18, 1993 <br /> Page 6 <br /> REMEDIAL OBJECTIVES <br /> To direct the design of remedial action, remedial objectives were identified. These <br /> objectives were formulated with attention to site characteristics, public health and <br /> safety, and protection of beneficial water uses. Objectives are distinguished as soil- <br /> and groundwater-based. <br /> o Soil: To the extent economically feasible, and using established <br /> technology,prevent the migration of petroleum hydrocarbons <br /> from soil beneath the referenced site. <br /> o Groundwater: Within physical and economic constraints: <br /> (1) eliminate the potential for exposure to groundwater with <br /> petroleum hydrocarbon concentrations in excess of acceptable <br /> compound levels, (2) eliminate hazardous conditions associated <br /> with the presence of petroleum hydrocarbon compounds in the <br /> subsurface environment, (3) protect the potential use of ground- <br /> water from the shallow water-bearing zone as domestic and <br /> municipal supply, and (4) initiate attenuation of petroleum hydro- <br /> carbon concentrations. <br /> For the most part, the soil objective applies to soils in the vadose zone immediately <br /> above the piezometric.surface. The vadose zone beneath the site appears to be of <br /> the heaviest impact of hydrocarbons in the vicinity of Wells U-1, U-2, and <br /> Boring U-C;between 5 and 6-1/2 feet below grade. Petroleum hydrocarbon <br /> concentrations in soil that do not pose a threat to groundwater will constitute the <br /> numerical cleanup goal for soil. Acceptable petroleum hydrocarbon <br /> concentrations in soil will be determined by using the environmental attenuation <br /> factor method proposed by Marshack (Marshack, 1989). <br /> The groundwater-based remedial objective applies to groundwater within a <br /> boundary delineation defined by acceptable compound levels. In this way, benefi- <br /> cial uses of groundwater outside the boundary will be protected, along with public <br /> health and%afety. The potential for hydrocarbon migration along groundwater <br /> flow lines to water-supply wells defines the primary exposure pathway. The associ- <br /> ated potential exposure route is the ingestion of impacted groundwater. Beneficial <br /> water use and public health protection require eliminating (reducing) the potential <br /> for exposure to groundwater with concentrations in excess of 1 ppb benzene, <br /> 680 ppb ethylbenzene, 100 ppb toluene, and 1,750 ppb xylenes. The aforemen- <br /> tioned concentrations constitute acceptable compound levels. <br /> 3100104/IRAP <br />