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l <br /> ' I ` 05 May 1997 <br /> C AGE-NC Project No 95-0112 <br /> Page 3 of 14 <br /> ' Quarterly ground water monitoring began in June 1992 Monitoring well MW-3 was not sampled <br /> between September 1987 and April 1995 due to the drop in ground water elevation at the site, MW-2 <br /> has riot been sampled since September 1987 due to the drop in ground water and the subsequent <br /> ' installation of MW-5 approximately 5 feet south of MW-2 Sampling of MW-6 and MW-8 was <br /> discontinued following the January 1996 monitoring due to their consistent up-gradient location and <br /> the non-detection of petroleum hydrocarbons Ground water flow toward the northwest was <br /> ' calculated for the June and August 1992 monitoring events Since that time,ground water has flowed <br /> consistently toward the south to southwest Past and current analytical results of ground water <br /> [ samples are included in Table 6 <br /> t <br /> 24 REMEDIATION WELL INSTALLATION <br /> ' n 18 August 1993 boiin RW-1 was installed near the southeast coiner of the building at a 15° <br /> 0 g � g g <br /> r angle fiom vertical toward the former UST location The boring was completed as a 4-inch diameter <br /> IC remediation well with screened PVC casing from 10 to 40 linear feet and from 45 to 501111ear feet <br /> Petroleum hydrocarbons were detected in soil samples collected during the well installation at <br />' concentrations as high as 12,000 ppm Analytical results of soil samples are summa)t.7ed on Table <br /> I The boring log is included in Appendix A The well installation was described in a Problem <br /> Assessment Report (PAR) dated January 1994 and prepared by GAS <br /> 25 SLUG TEST <br /> Slug tests were performed on monitoring wells MWA, MW-4, MW-6 and MW-7 by GAS on 18 <br /> November 1993 The tests included both water withdrawal and infection methods A pressure <br />' transducer was used to measure the water column in the wells during the tests and the results were <br /> graphed Hydraulic conductivity was calculated to range from 0 68 ft/day to 143 2 ft/day The <br /> aquifer transmissivity was calculated to range from 375 ft2/day to 7,150 ft2/day with an estimated <br /> [ aquifer thickness of 50 feet Details of the aquifer tests and calculations were presented in the PAR <br /> prepared by GAS <br /> 26 VAPOR EXTRACTION PILOT TEST <br /> A vapor extraction pilot test was conducted using vadose-zone well RW-1 as the extraction well The <br /> well was first tested on 16 November 1993, however, due to equipment failure,this test was aborted <br />' after only three hours and repeated on 17 December 1993 An effective radius of 25 to 35 feet was <br /> calculated for vapor extraction at the site High hydrocarbon concentrations were detected in air <br /> 4 samples collected during the pilot test Laboratory results of vapor samples collected during the test <br /> 1L <br />