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R603 UPDATE-12 12/22/92 <br /> filter in front of the vacuum pump. After the vapor stream j <br /> leaves the vacuum pump, it is pushed into the thermal oxidizer <br /> which oxidize the gasoline range hydrocarbon vapors at no less <br /> than 1400OF and no greater than 15500F. Influent samples are <br /> obtained from the exit of the pump and effluent samples are <br /> obtained from the stack of the thermal oxidizer. The gasoline <br /> range hydrocarbons are oxidized into heat, CO2 and water vapor, <br /> see UPDATE STATUS REPORT #5 <br /> A portable ambient air PID-GC (Photovac 10S50 packed column) is <br /> used at the site to sample the influent and effluent of the REMOX <br /> oxidizer and the individual wells (MW1, MW2-3 , MW10 and EX-4" ) , <br /> see Tables 2 , and 3 On November 19 , December 9 and 18 , 1992 , <br /> "Tedlar" bag samples were obtained of the influent and effluent <br /> of the REMOX incinerator and analyzed in WEGE' s portable <br /> laboratory utilizing the Photovac 10s50 PID-GC and Shimadzu FID- <br /> GC Just an influent sample was obtained on December 7, 1992 <br /> and influent from individual wells were obtained on December 9, <br /> 1992 These samples were analyzed for TFH and BTEX along with <br /> screening for Tetrachloroethylene (PCE) , Trichloroethylene (TCE) <br /> and 1, 2, -Dichloroethane (DCE) using a Shzmadzu GC-FID <br /> chromatograph mounted permanently in WEGE' s portable laboratory <br /> These compounds have the following retention times in the above <br /> chromatograph, DCE = 2 . 079 minutes, TCE = 3 023 minutes and PCE = <br /> 3 75 minutes Before sampling the wells or the system, a <br /> calabrant made from fresh gasoline is injected into the GC-PID <br /> and GC-FID The resulting chromatograms has numerous responses <br /> The microprocessor of the GC-PID and GC-FID computes the area per <br /> response in volt seconds and assigns a peak number and retention <br /> time The sum of all the responses are then used to obtain a <br /> mg/L per volt second calibrant factor, which is used to calculate <br /> mg/L as gasoline vapor from each analysis produced. Pounds per <br /> day can be computed using these mg/L values produced from the <br /> analysis of the different vapor recovery wells, the influent to <br /> the oxidizer, the pressure differential created at the orifice to <br /> determine flow rates for each well, and the influent to the <br /> oxidizer. The pounds per day values for each well and the <br /> influent are averaged with the preceding site visit' s pound per <br /> day value This figure is then multiplied by the number of hours <br /> the system operated between visits, to estimate the total pounds <br /> each well and the system has removed for that time period. This <br /> figure is added to the accumulated poundage of the previous visit <br /> to update the total pounds removed The effluent sample is <br /> computed in the same fashion, but also includes natural gas flow <br /> along with the influent orifice flow rate <br /> SAMPLING VAPOR STREAMS <br /> The vapor samples are obtained by attaching a dedicated air tight <br /> 010 <br /> ..`l port L.�. v rti r m r i n ra (-T9 <br /> OU cc syringe t o a sample port on C-he vapor rccover' - .....feN1.A (in__ <br /> the well side of the orifice plate) with air tight fitted <br /> polytubing. The sample port is opened and the syringe purged by <br /> pulling and pushing the syringe plunger several times Filling <br /> and depleting the syringe of that particular well' s vapor stream <br /> PAGE 6 <br />