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' Mr. Nuel Henderson <br /> Page 3 of 5 <br /> contains laboratory reports and chain of custody documentation. Attachment C contains <br /> graphs of contaminant concentrations over time. <br /> ' MTBE was below laboratory method detection limits ( DLs) in wells MW5, MW8, MW13B, <br /> MW 15A, MW 15C and MW 16B. MTBE was detected in wells MW 1 (6.4 parts per billion - <br /> ' ppb) and MW2 (26 ppb) for the first time. MTBE was also detected in MW3 (24,000 ppb), <br /> MW4 (8,100 ppb), MW7 (32 ppb), MW9 (1.5 ppb), MW12 (71 ppb), MW14 (38,000 ppb), <br /> ' MW15B (600 ppb) and MW16A (4,700 ppb). These wells are affected by MTBE releases <br /> originating at 101 S. Wilson Way and/or 130 S. Wilson Way. <br /> ' EDB was not detected in any of the wells sampled. 1,2-DCA was detected in wells MW 1, <br /> MW8, MW 12, MW13B, MW 15A, MW 15B and MW 15C. Detected concentrations of 1,2-- <br /> DCA ranged from 0.8 ppb in MW15A to 1,200 ppb in MW13B. Analytical results for <br /> ' gasoline oxygenates, EDB and 1,2-DCA are summarized in Table 3. Attachment B contains <br /> laboratory reports and chain of custody documentation. <br /> ' Vapor Extraction Wells <br /> TPHg and BTEX concentrations in the water sample collected from VW1 were within <br /> ' historical ranges. Benzene and toluene concentrations in the water sample collected from <br /> VW3 were the highest recorded since monitoring began. MTBE was not detected in well <br /> ' • VW1, but was detected in VW3 at a concentration of 51 ppb. The water sample collected <br /> from vapor well VW1 contained 1,2-DCA at a concentration of 1,100 ppb. This additive was <br /> not detected in the sample collected from VW3. TPHg and BTEX concentrations are <br /> summarized in Table 2. 1,2-DCA, EDB and gasoline oxygenate additive concentrations are <br /> summarized in Table 3. Attachment B contains laboratory reports and chain of custody <br /> documentation. <br /> 1 <br /> GROUNDWATER SAMPLING SUMMARY AND DISCUSSION <br /> ' • Water levels rose during this quarter. Groundwater elevation data continue to show a <br /> predominantly easterly-northeasterly groundwater flow direction. An upward vertical <br /> 1 gradient component was observed across the site. <br /> • Petroleum hydrocarbon concentrations in the wells affected by the onsite release were <br /> ' within historical ranges. The extent of groundwater contamination associated with the <br /> onsite release is stable and contaminant concentrations are stable to decreasing. <br /> ' • The plume of contamination originating from offsite source(s) is continuing to spread. <br /> High levels of MTBE persist in wells along the southern portion of the property. MTBE <br /> ' has also affected downgradient wells MW 12 and MW 15B where concentrations have risen <br /> over time. <br /> ' G.\GR0VN0ZEIR0EKIQMR000511q,n2005.doc <br />