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I <br /> A S S 0 C 1 A T E S I N C <br /> +sfr. <br /> 4.1.2 Petroleum Hydrocarbons in Soil <br /> A review of historical soil analytical data indicate the highest concentrations of petroleum <br /> hydrocarbons are generally present in borings MW4, SB-13, and SB-2 which are either <br /> immediately adjacent to the former UST or within 20 feet to the east of the former UST. <br /> Petroleum hydrocarbons at these locations were generally found at depths ranging from 10 to 15 <br /> feet bgs. <br /> Petroleum hydrocarbons were found further from the former UST at decreasing concentrations in <br /> borings MW2, MW3, MW6, S13-1 through SB-6, SB-11, and SB-12. At these locations <br /> ;- , petroleum hydrocarbons were detected at depths of approximately 15 feet bgs, <br /> In general, the soil samples collected at depths of 15 feet bgs were collected from below the <br /> groundwater table. <br /> 4.1.3 Mass Balance Calculations-Soil <br /> Using the analytical results presented in Table 1, ATC estimated the lateral extent of TPHd, which was <br /> then used to perform mass balance calculations to estimate the mass of residual soil contamination. <br /> The total mass of TPHd remaining in the soil is estimated to be approximately 1,605 pounds. This <br /> .......... estimate is conservative in the fact that it does not take into account degradation of TPHd in the soil <br /> samples collected in 1989 and 1993. Mass balance calculations are included in Appendix D. <br /> Ff <br /> k{q ' <br /> 4.2 Groundwater Conditions <br /> �= 4.2.1 Site H dro eolo <br /> Y g gY <br /> On October 18, 2000, static fluid levels were measured in monitoring wells MW1 through MW6. <br /> The water table elevation decreased an average of 0.77 feet since July 2000. Table 2 summarizes <br /> the water level data collected during the reporting period and provides previous data for <br /> comparison. <br /> �J <br /> A groundwater gradient map was created for the October 18, 2000 monitoring event (Figure 3) <br /> using groundwater elevation data from all the wells monitored. Figure 3 depicts generally a north <br /> groundwater flow direction at a magnitude of approximately 0.008 ft/ft or 42 ft/mile. <br /> During the period of investigation from 1989 to 2000 groundwater was measured at depths <br /> E ' ranging from 7.71 feet bgs to 17.34 feet bgs. During the period from 1995 to 2000 groundwater <br /> flow direction was consistently to the north at a gradient that ranged from 0.0029 to 0.018 ft/ft. <br /> r; The average gradient was approximately 0.0077 ft/ft. Prior to this period the gradient appeared <br /> to be affected by the presence of free product in well MW4. <br /> w:162574.021reporlslclosure-smith.doe 4 <br /> �s <br />