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I <br /> 14 February 2005 <br /> AGE-NC Project No 95-0128 <br /> Page 2 of 6 <br /> I In preparation for treatment additional ground water quantities,ground water discharge flow greater <br /> than 2 GPM,AGE replaced the GAC media The media change out occurred on 29 November 2004 <br /> to prevent a discharge and allow for enhanced flow through the adsorption media, which had been <br /> Utilized for three years and was experiencing high back-pressure A diagram of the remediation <br /> system is provided on Figure 2a <br /> In early October 2004,AGE began the utilization of extraction well EW-2, which produced higher <br /> volumes of groundwater than well EW-1 EW-1 was producing approximately 5 GPM for no longer <br /> than one-minute prior to faulting, which prevents over-amperage damage to the motor AGE has <br /> I attempted to install a pneumatic driven, low-flow pump in well EW-1, however excessive well <br /> siltation/sanding has occurred to the well The extraction well EW-1 was installed to a total depth <br /> of 45 feet bsg, which currently had screen exposed to approximately five feet of silt at the lower <br /> portion of the screen and two to three feet of sand and gravel above the lower silt contact <br /> documented at 40 feet bsg A re-development of the well will likely be required to collected the <br /> excessive sand generated during water extraction <br /> Based on effluent flow meter readings (Table 1), approximately 230,860 gallons of treated water <br /> were extracted and discharged to the City of Stockton sewer system during the third and fourth <br /> quarters of 2004 under City of Stockton Public Works Department(SPWD) Industrial Wastewater <br /> Discharge Permit No 01 On 13 October 2004, the waste water effluent flow meter required a <br /> change of the internal batteries and the meter total was re-set at zero This value will be added to the <br /> total gallons discharged during the reporting interval <br /> I2 12 Ground Water Extraction System Water Sampling Procedures <br /> Between May and December 2004, AGE collected water samples from valved ports located <br /> upstream (influent) and downstream (effluent) of the treatment unit The influent samples were <br /> collected in laboratory-supplied 40-milliliter (ml) EPA-approved volatile organic analysis (VOA) <br /> vials containing 0 5 ml 18% hydrochloric acid as a sample preservative, and 1-liter amber bottles <br /> without preservative Care was taken to ensure that visible air bubbles were not present In the vials <br /> after filling and capping <br /> Water sample containers were labeled with the sample designation,date,time,and sampler s initials <br /> Subsequently,the samples were logged on a chain of custody form,placed in a chilled container and <br /> transported to Cal T ech Environmental Laboratories (CTEL) a State of California Department of <br /> Health (DHS)-certified analytical laboratory The samples were analyzed for <br /> • Total petroleum hydrocarbons quantified as gasoline and as diesel (TPH-g and TPH-d) by <br /> EPA Method 8015 Modified, and Benzene, toluene, ethylbenzene and xylene (BTEX) and <br /> IAdvanced GeoEnvironmental,Inc <br /> I <br />