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A S S O C I A T E S I N !C <br /> 5 <br /> MW10, and three of the bonngs as vapor extraction wells VE1, VE2, and VE3 Groundwater <br /> monitoring well MW7 was replaced by vapor extraction well VE3 Soil samples collected from <br /> borings B101, B103, B104, VE3, and VE 1 contained detectable concentrations of TPHg and <br /> BTEX <br /> On August 16, 2003, the well casing elevations were re-surveyed by Condor Earth Technologies <br /> for elevation to within 0 01 foot under the supervision of a California licensed land surveyor and <br /> presented in Table 3 <br /> SAMPLING ACTIVITIES <br /> On May 27, 2004, groundwater samples were collected by ATC personnel from monitoring wells <br /> MW 1 through MW6, MW8, MW9, and the on-site domestic well Well MW 10 has an <br /> obstruction at approximately 20 feet bgs and was not sampled The locations of the monitoring <br /> wells are shown on Figure 2 Prior to collection of groundwater samples, the depth to water, pH, <br /> electrical conductivity, and temperature were measured in groundwater purged from the <br /> monitoring wells and recorded A minimum of three well casing volumes was purged from each <br /> well prior to sampling The wells were allowed to recover and samples were collected from each <br /> well using dedicated disposable bailers <br /> • The groundwater samples collected from each well were submitted to Argon Laboratories Inc <br /> (ELAP Cert No 2359), a California-certified analytical laboratory, for chemical analysis of <br /> TPHg and total petroleum hydrocarbons as diesel (TPHd) utilizing EPA method 8015B, BTEX <br /> utilizing EPA method 802113, and MTBE, tertiary butyl alcohol (TBA), d1-isopropyl ether <br /> (DIPE), ethyl tertiary butyl ether (ETBE), tertiary amyl methyl ether(TAME), 1,2-dichloroethane <br /> (1,2-DCA), and 1,2 d>bromoethane (EDB) utilizing EPA method 8260B Groundwater well <br /> purge and sample logs are contained in Attachment 1 <br /> GROUNDWATER FLOW DIRECTION <br /> Water level measurements collected from wells MWI through MW6, MW8, and MW9 on May <br /> 27, 2004, ranged from 7143 to 76 32 feet below the tops of the well casing elevations This <br /> represents a decrease in groundwater table elevation by an average of 1 68 feet from the February <br /> 5, 2004, sampling event The data from MW6 was not used for contouring because it is screened <br /> in a deeper interval The water level data were used to develop the groundwater elevation <br /> contour map (Figure 3) Assuming horizontal isotropic conditions, groundwater flow in the <br /> uppermost aquifer beneath the site on May 27, 2004, varied across the site, but was generally <br /> toward the southeast The average hydraulic gradient was calculated to be 0 04 ft/ft or <br /> approximately 211 ft/mile A summary of groundwater monitoring data 1s presented in Table 1 <br /> ANALYTICAL RESULTS <br /> • The groundwater samples collected from wells MW1, MW2, MW4, MW5, MW6, and MW9 and <br /> contained detectable concentrations of TPHg and BTEX constituents The groundwater samples <br /> S 1Enviromental125291\reports\?QR-2004 doc 2 <br />