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a <br /> CLOSURE REQUEST 5-31-94 <br /> Vapor Recovery System and Monitoring: <br /> During the latest confirmation soil sample drilling which <br /> occurred on February 2 , 1994, SB13 , SB14 and SB15 were converted <br /> into vapor extraction wells . These wells along with VSB5, VSB9, <br /> VSB11 and MW5 are presently be utilized for vapor extraction. <br /> These wells have been manifolded into the laterals of the above <br /> listed wells that are manifolded to a vapor extraction system <br /> with individual valved orifices for flow control and measurement . <br /> The wells are fitted with a PVC tee head with a locking air tight <br /> cap, for well access. The tee lateral (2 inch) is fitted with a <br /> 1/4 inch pipe to tubing fitting for obtaining vacuum/pressure and <br /> temperature readings. A pipe to hose 2 inch union is placed <br /> between the tee and the 2 inch PVC flex hose that connects the <br /> well to the extraction manifold. At the manifold the wells are <br /> connected to their own 2 inch PVC riser (36 inch in height) with <br /> an orifice plate and a gate valve at the top of the riser <br /> Vacuum/pressure ports are located on either side of the orifice <br /> plate . Each orifice (well) has its own manometer, calibrated in <br /> millimeters (mm) water, which are connected to the ports for <br /> continuous measurement of flow from a particular well . All the <br /> extraction wells are manifolded together above the gate valve to <br /> a set of two orifice risers that are in parallel before the <br /> vacuum pumps. After the vapor stream leaves the manifold, it is <br /> pulled into the pumps (two Rotron DR505 placed in series) and <br /> then into activated charcoal vapor scrubs . If breakthrough <br /> occurs through the 1st carbon (5 pounds per day or greater <br /> release of gasoline range hydrocarbons) , this carbon is removed <br /> from the system. The #2 carbon is then placed at the #1 position <br /> and a new carbon placed on the exhaust as the #2 carbon. <br /> A portable ambient air PID-GC (Photovac IOS50 packed column) was <br /> used at the site to sample, the influent and effluent of the <br /> system, and the influent from the various vapor extraction wells, <br /> for breakthrough of the carbon scrubs Before sampling the wells <br /> or the system, a calibrant made from fresh gasoline is injected <br /> into the GC-PTD The resulting chromatogram has numerous <br /> responses The microprocessor of the GC-PID computes the area <br /> per response in volt seconds, and assigns a peak number and <br /> retention time . The sum of all the responses are then used to <br /> obtain a mg/L per volt second calibrant factor. This factor is <br /> used to calculate mg/L as gasoline vapor from each analysis . <br /> Pounds per day can be computed using these mg/L values, and the <br /> pressure differential created at the orifice (flow rate) for each <br /> well, and total influent . Since September 25, 1992, tedlar bag <br /> samples are obtained and brought back to be analyzed in the WEGE <br /> portable laboratory This is necessary due to long eluting time <br /> (analysis time increased from 10 minutes per sample to 30 minutes <br /> per sample) needed per analysis using the 10s50 (all early <br /> eluting compounds have been removed by vapor extraction) . The <br /> pounds per day values for each well and the influent are then <br /> averaged to the corresponding values from the preceding site <br /> visit and then multiplied by the number of days the system <br /> operated between visits to determine the total pounds removed for <br /> each well and for the total system for that time period. This <br /> page34 <br />