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CVV V9 <br /> A S 5 0 C I. A T E S I N C . <br /> detected in the groundwater sample collected from soil boring SBI. The January 1998 <br /> subsurface investigation results are detailed in ATC's Summary Report for Subsurface <br /> Investigation, dated February 4, 1998. <br /> In September 1998, ATC supervised the excavation of approximately 70 tons of impacted soil. <br /> The soil was transported and disposed of at an appropriate landfill on the same day it was <br /> excavated. The excavation was limited on two sides by buildings and overhead lines. <br /> Confirmation samples collected from the excavation indicated there was residual contamination <br /> remaining. Also in September 1998, ATC supervised the advancement of four soil borings <br /> around the former excavation area. Three of the borings were completed as groundwater <br /> monitoring wells. Analytical data indicated the soil and groundwater at the site is impacted with <br /> total petroleum hydrocarbons as stoddard solvents (TPHss). The September 1998 subsurface <br /> investigation results are detailed in ATC's Summary Report of Soil Excavation and Additional <br /> Subsurface Investigation, dated December 3, 1998. <br /> SAMPLING ACTIVITIES <br /> On March 10, 2000, groundwater samples were collected by ATC Associates personnel from <br /> monitoring wells MW1 through MW3. The locations of the monitoring wells are shown on <br /> Figure 2. Prior to collection of groundwater samples, the depth to water, pH, electrical <br /> conductivity, and temperature were measured in the monitoring wells and recorded. A minimum <br /> of three well casing volumes were purged from each well prior to sampling. The wells were <br /> allowed to recover and samples were collected from each well using dedicated disposable bailers. <br /> Groundwater well purge and sample logs are contained in Attachment 1. <br /> The groundwater samples collected from each well were submitted to State-certified Argon <br /> Laboratories (ELAP Cert. No. 2358) for chemical analysis of TPHg, TPHd, and TPHss utilizing <br /> EPA Method 8015 modified, and benzene, toluene, ethylbenzene, and xylenes (BTEX) utilizing <br /> EPA Method 8020. <br /> GROUNDWATER FLOW DIRECTION <br /> Water level measurements were collected from wells MW1 through MW3 on March 10, 2000. <br /> Water levels ranged from 23.69 to 24.29 feet below the tops of the well casings elevation, <br /> representing an average increase in the water table elevation of approximately 1.68 feet since <br /> December 1999. The water level data were used to develop the groundwater elevation contour <br /> map (Figure 2). Assuming that horizontal isotropic conditions prevail, groundwater in the <br /> uppermost aquifer beneath the site flowed towards the east-northeast. The average hydraulic <br /> gradient on March 10, 2000 was calculated to be 0.002 ft/ft or approximately 11 ft/mile. A <br /> summary of groundwater monitoring data is presented in Table 1. <br /> w:%]72951quar lyl l qr-2000.doc 2 <br />