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R603 UPDATE-13 2/15/93 <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 Shimadzu 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 /> calibrant made from fresh gasoline is infected 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 /> 60 cc syringe to a sample port on the vapor recovery manifold (on <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 /> Then the syringe is filled, the sample valve closed, and forceps <br /> are clamp onto the soft polytubing to create an air tight seal <br /> before removing the syringe from the sample port . Once the 60 cc <br /> syringe is removed with the clamped polytubing attached, the <br /> L t t-L. roat- nYGQ ail L71 thin IIP <br /> plunger l�S Yubileu inl..V 411c �"y'r ii�ge 'Co4v Ca..�-u.r�- <br /> syringe and released to allow the collected vapors to reach <br /> equilibrium A small dedicated needle attached to a dedicated 1 <br /> cc syringe is then inserted into the 60 cc syringe via the soft <br /> tubing for obtaining the sample to be injected into the PID-GC <br /> Again the 1cc syringe is purged numerous times before filling it <br /> with the sample. All but 0 . 5 cc of the sample is ejected into <br /> the air before infecting the remaining 0 5 cc syringe sample into <br /> the GC--PID (the calibrant infection is 0 . 5 cc) . Once the <br /> chromatogram is recorded an instrument blank is run prior to the <br /> PAGE 6 <br />