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F removed from MW-1 during development The remaining monitor wells were <br /> all developed by removing approximately 55-gallons of water from each <br /> well <br /> As previously stated, soil borings SB-1 through -5 were all drilled to <br /> 17 5 feet below ground surface These _borings were backfilled with the <br /> aforementioned cement grout mixture from total depth to ground surface <br /> All grouting operations were witnessed by a SJLHD site inspector <br /> Groundwater Sampling <br /> Groundwater samples were collected for TPH-G and VOA analysis by Modified <br /> EPA Method 8015 and EPA Method 602, respectively, from each monitor well <br /> Monitor wells MW-1, -3, and -6, which showed the presence of elevated <br /> concentrations of VOAs, were also sampled for ethylene dibromide (EPA <br /> Method 504) and organic lead (tetraethyl lead) The primary supply well <br /> and the backup supply well at the site were sampled for VOCs (EPA Methods <br /> 601 and 602) , ethylene dibrom3.de (EDB) and total volatile hydrocarbons <br /> (Modified EPA Method 8015) <br /> Monitor wells were allowed to equilibrate following construction for a <br /> period of not less than 12 hours prior to groundwater sampling Prior to <br /> a sampling, the top-of-casing elevation for each well was surveyed relative <br /> mil to an assumed datum of 20 feet mean sea level ( <br /> MSL) , as derived from the United States Geological Survey topographic map <br /> of the Lodi North Quadrangle, California and depth to water measurements <br /> were taken to determine groundwater elevations at each well Before <br /> sampling, monitor wells MW-1 through -8 were purged by pumping <br /> approximately 55 gallons of water from each well Monitor wells MW-9 and <br /> -10 were bailed dry and allowed to recharge for approximately 5 to 10 <br /> minutes prior to collecting groundwater samples Groundwater samples were <br /> collected from each monitor well with disposable, polyethylene, non- <br /> reactive bailers Samples were collected at the supply wells from steel <br /> sampling ports after purging each well for approximately 15 minutes <br /> Water samples were tranferred to appropriate sample containers by filling <br /> from the bottom to top of the container to minimize sample aeration Each <br /> sample container was individually labeled and placed on ice in a thermally <br /> insulated chest All water samples were delivered to the appropriate <br /> analytical laboratory with an accompanying chain-of-custody form <br /> Analytical Services <br /> Analyses for TPH and VOAs in soil and groundwater samples were performed <br /> by Weston Analytical Laboratory of Stockton, California Weston also <br /> conducted EDB analyses of groundwater samples taken from monitor wells MW- <br /> 1, -3, -6, and the primary supply well McLaren Analytical Laboratory of <br /> Rancho Cordova, California performed the analyses of water samples taken <br /> from the back-up supply well for VOCs, EDB, and total volatile <br /> hydrocarbons and analyzed additional water samples from the primary supply <br /> well for total volatile hydrocarbons <br /> 12 <br />