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i <br /> SVESVESystem <br /> ' The current SVE equipment (i e , 300 standard cubic feet per minute (SCFM) thermal oxidizer) was <br /> installed at the site on April 7, 2005, replacing a previous SVE unit The SVE unit was connected to the <br /> existing 500-gallon propane above ground storage tank (AST) for supplemental fuel supply, necessary <br /> ' hoses, pipes, gauges to transfer the propane, subsurface piping and wellhead connections between the <br /> SVE remediation wells, the AS remediation wells and the fenced remediation equipment compound <br /> ' Four SVE remediation system wells (VW1 through VW4) were originally utilized at the site VW1 is <br /> screened between 10 and 30 feet bgs VW2 is screened between 20 and 35 feet bgs VW3 and VW4 were <br /> screened between 15 feet bgs and 25 feet bgs Each SVE wellhead connection includes a gate valve, <br /> ' vacuum gauge, sampling port,and flow rate measurement port <br /> After the initial start-up operations for the original SVE system, VW3 was taken off line to reduce water <br /> production and VW4 was partially closed off but remained on line In July of 2004, the completions of <br /> VW1 and VW2 were altered to further reduce produced water These wells now include stingers set at <br /> approximately 28 feet bgs and 32 feet bgs, respectively. <br /> MW 1 was converted to a vapor extraction well on February 10, 2004 The well completion of MW 1 was <br /> altered with a stinger set at approximately 32 feet bgs <br /> Water Treatment System <br /> The SVE/AS system, groundwater treatment and discharge system (as previously configured) were started <br /> up on December 20, 2003 A water treatment system is required for the produced water associated with <br /> the SVE wells <br /> Components of the water treatment system include the knockout tank, located within the remediation <br /> ' compound, one 1,000-gallon drop tank, three transfer pumps, two 2,000 pound canisters connected in <br /> series containing aqueous-phase granular activated carbon (GAC), associated piping, control valves, <br /> pressure gauges, flow meters, Instrumentation and controls Treated water is pumped from the effluent <br /> end of the lag canister Into a 100-gallon tank, where it is discharged to the sanitary sewers stem located <br /> ' g �Y Y <br /> on the south side of the on site building <br /> ' During Initial start up of the original vapor extraction system, approximately 25 gallons of groundwater <br /> per hour were extracted from the four vapor wells (VWI —VW4) ATC closed the valves on VWI and <br /> VW2 and only extracted from VW3 and VW4, which are screened approximately two feet above the <br /> ' current water level Seven gallons of groundwater per hour were extracted from VW3 and VW4 <br /> To operate the vapor extraction system more efficiently, ATC modified the vapor extraction system to <br /> ' include groundwater treatment and discharge to the City of Stockton sewer system (This is the <br /> groundwater that accumulates during operation of the vapor extraction side of the system ) ATC <br /> submitted the necessary permit application Information for the discharge of treated groundwater and on <br /> November 6, 2002 the City of Stockton Department of Municipal Utilities (DMU) issued the <br /> Groundwater Discharge Permit (GDP) Following the issuing of the GDP, approximately 50 feet of 3- <br /> inch diameter, ABS pipe was placed on the surface of the site from the remediation compound to a <br /> discharge point located inside the bathroom of the on-site building The ABS pipe was connected to the <br /> existing sewer discharge line by a California licensedurin lumber dthe week of November 25, 2002 <br /> P g <br /> s lenviro1625961quart1y\1gr-2006 doc 4 ATC ASSOCIATES INC <br />