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• AS S O C I ATE S IN C . <br /> In January 2003, GHH Engineering, Inc. (GHH) advanced three cone penetrometer borings and <br /> three soil borings to depths ranging from 104 feet bgs to 122 feet bgs. <br /> In May 2003, GHH advanced four soil borings, MW6a, MW6b, MW7a, and MW7b to the east of <br /> the site. These borings were completed as well clusters with MW6 and MW7a advanced to a <br /> depth of approximately 75 feet bgs, and MW6b and MW7b advanced to a depth of <br /> approximately 94 feet bgs. GHH also installed well EW1 in the southeast portion of the site. <br /> Site activities were summarized in GHH's Second Quarter 2003 Groundwater Monitoring <br /> Report and Additional Assessment Report, dated June 2003. <br /> In January 2004, an ATC geologist supervised the installation of five spargepoint wells <br /> associated with an ozone injection system. Each spargepoint has a shallow and deep injection <br /> well for the ozone. The shallow spargepoints were installed to a depth of approximately 75 feet <br /> bgs and the deep spargepoints were installed at a depth of approximately 108 feet bgs. From <br /> February 17 to approximately April 20, 2004, an ATC geologist supervised the installation of <br /> groundwater monitoring wells MW6c, MW7c, MW8, MW9a, MW9b, MW9c, MW10a, MW10b, <br /> and MWIOc. <br /> SAMPLING ACTIVITIES <br /> On June 3, 2004, ATC personnel collected groundwater samples from monitoring wells MW1 <br /> through MW5, MW6a, MW6b, MW6c, MW7a, MW7b, MW7c, MW8, MW9a, MW9b, MW9c, <br /> MW10a, MW10b, MW10c and EWL The locations of the wells are shown on Figure 2. Prior to <br /> collection of groundwater samples, the depth to water was measured in MW1 through MW5, <br /> MW6a, MW6b, MW6c, MW7a, MW7b, MW7c, MW8, MW9a, MW9b, MW9c, MW10a, <br /> MW10b, MWIOc and EW1 and the pH, electrical conductivity, and temperature were measured <br /> in groundwater purged from the monitoring wells and recorded. A minimum of three well casing <br /> volumes were purged from each monitoring well prior to sampling, except for wells MW6c, <br /> MW7c, MW9b, and MW10c which were bailed dry. Approximately 1.2, 1.3, 1.4 and 2.1 well <br /> volumes of water were removed from MW6c, MW7c, MW9b, and MW10c, respectively. The <br /> wells were allowed to recover and samples were collected from each well using disposable <br /> polyethylene bailers. After samples were collected, dissolved oxygen (DO) concentrations were <br /> measured. <br /> The groundwater samples collected from each well were submitted to State-certified Argon <br /> Laboratories Inc. (ELAP Cert. No. 2359) in Ceres, California for chemical analyses of total <br /> petroleum hydrocarbons as gasoline (TPHg) and total petroleum hydrocarbons as diesel (TPHd) <br /> _ .__utilizing.EPA Method 8015B; benzene, toluene, ethylbenzene, and xylenes (BTEX) utilizing = <br /> EPA Method 802113; and methyl tertiary butyl ether (MTBE), ethyl tertiary butyl ether (ETBE) <br /> di-isopropyl ether (DIPE), tertiary amyl ether (TAME), tertiary butyl ether (TBA), 1,2- <br /> dichloroethane (1,2-DCA), and 1,2-dibromoethane (EDB) utilizing EPA Method 8260B. <br /> • Groundwater well purge and sample logs are contained in Attachment 1. <br /> S:1268231QM reports12004 2QR.doc 2 <br />