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elevations from the three groundwater monitoring wells. Soil samples will be analyzed for <br /> total petroleum hydrocarbons and MTBE. This information will be used to determine the <br /> extent of contamination and will aid in the design of remediation. <br /> 4.0 DISCUSSION <br /> 4.1 Waste Oil USTs <br /> S-P's Work Plan to determine the extent of contamination from two former waste oil USTs <br /> called for the installation of two bore holes; one upstream and one downstream from the <br /> tanks. S-P reported groundwater flow in a northeasterly direction to locate these two bore <br /> holes. The plan was modified in the field to include four bore holes, one of which was then <br /> r , converted into a groundwater monitoring well. Contamination from waste oil and gasoline <br /> l (TPHg, BTEX and MTBE) was found in both the soil and the groundwater samples. Bore <br /> Ir hole locations are shown in Figure 2 and the analytical results are listed in Appendix A, <br /> Table 1. <br /> A review of the analytical results indicates that, when the work was completed, soil <br /> contamination was generally confined to the area immediately adjacent to the two USTs. <br /> Groundwater contamination existed at all locations that were analyzed (MW-2, B-3 and B- <br /> 4). Soil contamination included both oil (TPHo) and gasoline, while groundwater <br /> contamination was confined to gasoline. Since this time, oil has reached the groundwater <br /> at MW-2, as evidenced by an attempted sampling in September 1998. <br /> Soil samples showed extremely little or no MTBE present. Slightly different results were <br /> obtained from the two analytical procedures — MTBE levels were either 0.06 ppm to 0.09 <br /> ppm or ND (detection limit = 0,005 ppm) depending upon which procedure is accepted. In <br /> any case, the low levels of MTBE in soil are generally consistent with the behavior of MTBE, <br /> BTEX and oil. MTBE sorbs only weakly into the soil and is very soluble in water (50,000 <br /> ppm versus 1780 ppm for benzene, the next most soluble component in gasoline). Oil <br /> sorbs more strongly in soil and is relatively insoluble in water. BTEX is located in between <br /> these two extremes. This results in partitioning of the various components between the soil <br /> and the groundwater. It seems reasonable to conclude that (1) the former USTs were the <br /> source of both used oil and gasoline contamination, (2) the extent of contamination in the <br /> soil has been determined and (3) the contamination in the groundwater has probably <br /> Environeering, Inc. Project No. 98-012.01 3 <br />