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R604 .UPDATE 26 1-21-1994 <br /> flex hose that connects the well to the extraction manifold. At <br /> the manifold the individual wells are connected to their own 2 <br /> inch PVC riser (36 inch in height) with an orifice plate and a <br /> gate valve at the top of the riser Vacuum/pressure ports are <br /> located on either side of the orifice plate Each orifice (well) <br /> has its own manometer (calibrated in millimeters (mm) water) <br /> which are connected to the ports for continuous measurement of <br /> flow from a particular well All the extraction wells are <br /> mansfolded together above the gate valve to a set of two orifice <br /> risers that are in parallel before the vacuum pumps . After the <br /> vapor stream leaves the manifold, it is pulled into the pumps <br /> (two Rotron DR505 placed in series) and then into activated <br /> charcoal vapor scrubs If breakthrough occurs through the 1st <br /> carbon, this carbon is removed from the system The #2 carbon is <br /> then placed at the #1 position and a new carbon placed on the <br /> exhaust as the #2 carbon <br /> A portable ambient air PID-GC (Photovac 10S50 packed column) was <br /> used at the site to sample for breakthrough of the carbon scrubs, <br /> the influent and effluent of the system, and the influent from <br /> the various vapor extraction wells Before sampling the wells or <br /> the system, a calibrant made from fresh gasoline is infected into <br /> the GC-PID The resulting chromatogram has numerous responses <br /> The microprocessor of the GC-PID computes the area per response <br /> in volt seconds, and assigns a peak number and retention time <br /> The sum of all the responses are then used to obtain a mg/L per <br /> volt second calzbrant factor This factor is used to calculate <br /> mg/L as gasoline vapor from each analysis Pounds per day can <br /> be computed using these mg/L values, and - the pressure <br /> differential created at the orifice (flow rate) for each well, <br /> and total influent Since September 25 , 1992 , tedlar bag samples <br /> are obtained and brought back to be analyzed in the WEGE portable <br /> laboratory This is necessary due to long eluting time (analysis <br /> time increased from 10 minutes per sample to 30 minutes per <br /> sample) needed per analysis using the 10s50 (all early eluting <br /> compounds have been removed by vapor extraction) . The pounds per <br /> day values for each well and the influent are then averaged to <br /> the preceding site visit ' s pound per day value and then <br /> multiplied by the number of days the system operated between <br /> visits to estimate the total pounds each well and the total <br /> system has removed for that time period This poundage is then <br /> added to the accumulated poundage of the previous visit to update <br /> the total pounds removed to date, see Table 3 and Appendix C <br /> Sampling Vapor Streams <br /> The vapor samples are obtained by attaching a dedicated air tight <br /> soft polytubing to a sample port on the well side of the orifice <br /> plate on the vapor recovery manifold The tubing is then <br /> connected to a tedlar bag placed inside a vacuum sampler The <br /> sample port is then opened and the vacuum placed on the tedlar <br /> bag from the sample vessel allows the tedlar bag to fill with the <br /> vapor stream from that particular sample port . once the tedlar <br /> bag is full the valve is closed and the vacuum removed from the <br /> sample vessel The tedlar bag contains an air tight locking <br /> Septum valve which is then closed and locked to secure the vapor <br /> sample A small dedicated needle attached to a dedicated 1 cc <br /> page 5 <br />