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' encountered north and east of theroPerty in the down-gradient direction from the suspected <br /> p <br /> former source of the unauthorized hydrocarbon release, but was not well constrained in these <br />' directions These factors necessitate installation of the additional ground water monitoring wells <br /> A vapor extraction test was conducted in December 1993 Since that time, ground water has <br />' risen from approximately 55 feet bsg to as high as 30 feet bsg, reducing the vertical extent of the <br /> vadose zone open to the screened interval of the vapor extraction well The rise of ground water <br />' elevation has also eliminated most of the coarse-grained soil from the vadose zone, leaving <br /> predominantly fine-grained soil in contact with the reduced open screened interval of the vapor <br /> extraction well These changes can potentially drastically reduce the zone of influence of the <br />' vapor extraction well(s) and reduce the concentrations of hydrocarbon vapor recovered by the <br /> extraction process <br />' On 29 and 30 April and 01 May 1998, seven probe borings (B 13 through B 19) were advanced <br /> off-site of the subject property to collect soil and grab ground water samples as part of on-going <br /> assessment of the release of fuel hydrocarbons from the former UST facility TPH-g, TPH-d and <br /> I BTEX were not detected in any of the soil samples analyzed, however, MTBE was detected at <br /> 180 micrograms per kilogram (µg/kg) in the soil sample from boring B 16 at a depth of 40 feet <br /> bsg TPH-g was not detected in any of the grab water samples collected, but TPH-d was detected <br /> in seven of the eight grab water samples at concentrations as high as 1,200 pg/l Various BTEX <br /> compounds were detected in the grab water samples from borings B 13, B 14 and B 17 at <br /> concentrations as high as 14 micrograms per liter (µg/1), benzene was detected only in the <br />' sample collected from boring B13 at a depth of 60 feet bsg, at a concentration of 0 61 µg/l In <br /> addition, MTBE was detected in seven of the eight grab ground water samples collected at a <br /> maximum concentration of 1,400 pg/l in sample B 16-H2O TBA was detected in sample B 13- <br /> H2OB at a concentration of 16 µg/l <br /> On 20 March 2001, ground water extraction well EW-1 was installed at the site for performance <br /> of a ground water pumping test At the regulatory directive of the EHD a twelve-hour aquifer <br /> pump test was performed on 27 March 2001 to assess the general ground water aquifer <br /> characteristics and to assess aquifer response to ground water extraction at a constant pumping <br /> rate utilizing well EW-1 for ground water extraction and wells MW-1, MW-2, MW-4, MW-5 <br /> and MW-6 and vapor well VW-1 as observation wells Three ground water samples were <br /> collected from the extracted ground water and purged ground water was containerized in an on- <br /> site 6,500-gallon poly tank The implications from the March 2001 aquifer ground water <br /> pumping test are <br /> • Ground water draw-down of at least 11 15 feet was observed in extraction well EW-1 <br /> following 700 minutes of continuous pumping (5 GPM), ground water draw-down was <br /> observed in well MW-5 (located 15 feet to the east) at 1 1 feet, well MW-4 (located 60 <br /> feet toward the southeast) at 0 1 feet, well MW-6 (located 50 feet toward the north- <br /> northwest) at 0 12 feet and in well vapor well VW-I (located 60 feet toward the west) at <br /> 0 06 feet <br /> . Utilizing a semi-logarithmic plot of ground water draw-down vs observation well <br /> distance to pumping well, a best-fit line can be utilized to project a radius of influence of <br /> I <br />