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4.0 CONCLUSIONS AND RECOMMENDATIONS <br />' This phase of environmental corrective action included the installing, surveying and sampling <br /> three groundwater monitoring wells Soils encountered beneath the site consist of a fining- <br /> upward sequence of fine-grained siliciclastic sediments The depth to static groundwater beneath <br /> the site ranges from 7 74 to 8 16 feet bgs Groundwater flow is to the north at a relatively low <br /> gradient of 0 004 foot/foot <br /> _ <br /> Only the groundwater sample collected from MW-2 contained detectable concentrations of <br /> petroleum hydrocarbons The only compound detected at MW-2 was TPH-as-diesel at 140 µg/I <br /> As such, the plume of impacted groundwater appears to have migrated from the area of the <br /> former USTs at least 30 feet to the northeast Based on the presence of free product previously <br /> observed in close proximity to the former USTs and the relatively low concentration of diesel in <br /> groundwater at MW-2, contaminant migration appears to be slow and probably stable This is <br />' supported by the relatively flat groundwater gradient <br /> Groundwater testing for physiochemical and microbial parameters indicated that nitrate <br /> concentrations and both general and selective microbial populations are relatively low However, <br /> the relative percentage of selective degraders to the total number of heterotrophs is high These <br /> results suggest that the existing microbes are capable of degrading the contaminant The <br /> population of naturally occurring bio organisms would likely be enhanced by the addition of <br /> nutrients, namely nitrate and oxygen <br /> No water wells or other sensitive receptors appear to be threatened by the plume of impacted <br /> groundwater The two wells identified as closest to the site could not be physically located <br /> Based on the results of the well installation and sampling and water well survey, Ramage <br /> Environmental recommends the following course of environmental corrective action <br /> 1 Monitor and sample groundwater from the three monitoring wells on a quarterly basis for at <br /> least three more quarters The groundwater samples should be analyzed for TPH-as- <br /> gasoline, BTEX and MTBE by Modified EPA Methods 8015 and 8020 Since the other <br /> oxygenate compounds are absent, no further testing by EPA 8260 is necessary <br /> 2 Based on the results of four quarters of groundwater monitoring and sampling and on the <br /> results of previous soil and groundwater grab samples collected at the site, evaluate the risk <br /> posed by residual petroleum hydrocarbons on human health and the environment <br /> 3 Based on the findings of the risk assessment, request regulatory closure or proceed with <br /> further evaluation of possible remedial alternatives <br /> 12 <br />