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Geologual Technics Inc Page 5 <br /> 1" Quarter 2004 Groundwater Momtonng Report <br /> Project No 507 2 <br /> May 19,2004 <br /> 1 <br /> • Deep well MW-109 did not contain contaminants above the laboratory reporting limits <br /> for the fourth consecutive event The reduction in contaminant concentrations from the <br />' first sampling event on June 1, 2001 is noted and sufficient monitoring has been <br /> perfonned to conclude that it was probably a drilling artifact or the bottom of the <br />' groundwater plume <br /> • Figure 4 illustrates the relationship between groundwater elevation and TPH-G <br /> concentrations in well MW-9 (located in the core of the plume) An inverse trend was <br /> ' consistent for the first four monitoring events, and then it was parallel between March <br /> 2001 and December 2002,but since has had a variable relationship <br /> • Trend lines added to the data in Figure 4 show that as the groundwater elevation has <br /> ' lowered since 1999 that the concentration of TPH-G has increased This suggests that <br /> concentration is directly related to groundwater level at the site <br /> ' • Figure 5 illustrates the relationship between groundwater elevation and TPH-G <br /> concentrations in well MW-5 (located up/cross gradient of the core of the plume) An <br /> inverse trend was consistent for the first four monitoring events, and then it was parallel <br /> between March 2001 and December 2002, but since has had a variable relationship <br /> • Figure 6 indicates an inconsistent relationship between groundwater elevation and <br /> contaminant concentrations in well MW-6 No data is included for the December 2002 <br /> event due to the well's inaccessibility <br /> e Figures 4, 5, & 6 illustrate that the concentrations of TPH-G increase as the water table <br /> decreases, suggesting that the plume is stable and not being degraded by natural <br /> biodegradation causes It also suggests that the vadose zone soils contain abundant <br /> mobile phase petroleum product <br /> ' e The groundwater gradient is relatively flat and the direction of groundwater flow has <br /> varied during the course of the investigation <br /> ' 0 Oxidation-Reduction Potential (ORP) was measured (Table 4) and the results suggest <br /> that all of the wells sampled are either in the core of the contamination plume or are <br /> immediately down gradient from the plume and within the halo of reaction depleted <br /> water caused by biodegradation of the contaminants <br /> Figure 7 is a contour map indicating the TPH-G concentrations on March 19, 2004 The <br /> groundwater plume is localized in the vicinity of the former UST excavation The bulls- <br /> eye pattern to the TPH-G contour map in Figure 7 shows that the center of the plume has <br /> not moved from its source and suggests that contaminant migration may be occurring <br /> primarily by diffusion with a slight influence by advection <br /> 1 <br />