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Geological Tecfmics Inc Page 5 <br />' Groundwater Monitoring Report <br /> Project No 425 2 <br /> • May 20,2002 <br /> o Groundwater levels have previously exhibited a trend of decreasing elevation This <br /> situation may have stabilized or reversed since September 2000- see Figure 8 <br /> TPH-G and benzene concentrations in MW-1 exhibited a sharp increase to the highest <br /> levels recorded in the investigation This well lies in the predominant up gradient <br /> 1 direction from the former UST field and the reason for this anomaly is not known See <br /> Figure 4 for a graph of Benzene and TPH-G versus time and Figure G for the <br /> distribution of TPH-G <br /> ' ® BTEX & TPH-G concentrations in MW-2 continue to decrease since the impacted soils <br /> in the vicinity of the former USTs were excavated in July 2001 See Figure 5 for graph <br /> of Benzene and TPH-G versus time and Figure b for the distribution of TPH-G <br /> ' ® Figure 7- Groundwater Elevation vs Time MW-2 demonstrates a general trend of <br /> increasing TPH-G concentration with decreasing groundwater elevation <br /> a Contaminant concentrations in wells MW-4 and MW-5 exhibit a stable trend <br /> o For the sixth consecutive event, wells MW-102 and MW-202 did not contain <br /> contaminant concentrations above the laboratory reporting limits <br /> G All three of the domestic wells were non-detect for the event <br /> o Oxidation-Reduction Potential (ORP) was measured (Table 5 & Figure 9) The results <br /> suggest that well MW-2 is in the core of the contamination plume or is immediately <br /> down gradient of the plume Negative ORP values indicate that the wells are within the <br /> halo of reaction depleted water caused by biodegradation of the contaminants For the <br /> February 22, 2002, event, seven water table wells had negative ORP values <br /> 1 <br /> 3.0 CONCLUSIONS AND RECOMMENDATIONS <br /> The following conclusions have been drawn regarding the status of the groundwater at this <br /> ' site and recommendations for future work <br /> Conclusions <br /> ' 1 The water table groundwater gradient historically flowed in a northerly direction at <br /> about 0 002 ft/ft prior to May 1998 However, since that time, the gradient has <br /> fluctuated from north to northeast <br /> ' 2 The intermediate depth groundwater has flowed easterly, with two shifts to southeast <br /> during September 2000 & September 2001 The direction of north for the December 3 <br /> event was anomalous, however the December 21 event was again consistent with the <br /> ' historical data showing an easterly flow <br /> 3 Vertical groundwater gradients have been found to be flowing upward during winter and <br /> early spring and downward during late spring and summer This may be due to the <br /> ' annual cycle of the groundwater pumping needs of the community <br /> 4 The dominance of upward vertical flow of groundwater may be the primary reason the <br /> contaminants have not impacted the drinking water aquifer During periods of heavy <br />