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� r i • _ <br />' Several changes are noteworthy <br /> a)for the first time, groundwater is not shallowest in MW-7 <br />' b)for the first time, groundwater is shallower in MW-5 than in MW-3 <br /> c)for the first time, groundwater is not at the same depth in MW-2 and MW4 <br />' As a result of these irregularities, the groundwater gradient appears to be strikingly different from the <br /> normal situation (Figure 6) Rather than the usual groundwater low("trough") situated around MW-5, <br /> there appears to be a high surrounding the deep extraction well, with flow off this high toward the <br /> southeast, south, and southwest If subsequent monitoring confirms this pattern, it could indicate that <br /> air sparging into VE-1 has mounded the groundwater and locally reversed the groundwater flow <br /> direction The primary flow direction, however, continues to be toward the southeast <br /> 5.4 Groundwater Contamination <br /> t As in the previous five quarters, contaminants were detected in MW-5 (Table 2) The benzene and <br /> TPH-g concentrations reached a peak m May, when the water table was high, but declined as the water <br /> table dropped in the third quarter <br /> 1 <br /> 6.0 CONCLUSIONS AND RECOMMENDATIONS <br /> Approximately 3,852,600 cu ft of vapors were withdrawn and combusted between July 1 and <br /> September 30, 1996 VOC concentrations (as measured by PID) in the shallow well vapor stream <br /> declined approximately 50% from the previous quarter, whereas concentrations in the deep well <br /> remained very low and constant The mean VOC concentration measured in the shallow well during <br />' the 9 monitoring events was 680 ppm Using this value, we calculate that 690 pounds of hydrocarbons <br /> were destroyed <br />' Contaminant concentrations in the groundwater sample from MW-5 were lower in the third quarter <br /> than in the second quarter of the year, repeating the pattern seen in 1995 This is probably due largely <br /> to the seasonal fall in the static water level, separating groundwater from residual gasoline in the <br />' vadose zone However, the TPH-g concentration in the third quarter of 1996 was only 36% of that in <br /> the third quarater of 1995, hence, it is possible that there has been an absolute decline in concentration <br />' Depth-to-groundwater measurements in this quarter suggest an anomalous change in the groundwater <br /> gradient that could be due to air sparging activities Because the flow pattern appears to differ so <br /> radically from what has been seen in previous quarters, we suggest that the depth to groundwater be <br />' measured again in October to check the validity of the August data <br /> In the previous report we speculated that vapor concentrations would increase as the static water level <br />' drops during the second half of the year and the capillary fringe and "smear zone" become more <br /> exposed This did not happen--vapor concentrations declined 'somewhat from their second-quarter <br /> levels and remained fairly constant This is probably a good sign, indicating that remediation is nearing <br />' completion <br /> 5 <br /> 1 � <br />