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ARCHIVED REPORTS XR0006466
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0006466
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Last modified
8/21/2019 4:59:38 PM
Creation date
8/21/2019 2:52:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006466
RECORD_ID
PR0519189
PE
2950
FACILITY_ID
FA0014347
FACILITY_NAME
CURRENTLY VACANT
STREET_NUMBER
6425
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
09741031
CURRENT_STATUS
02
SITE_LOCATION
6425 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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R603 UPDATE-11 11/19/92 <br /> • <br /> samples were obtained of the influent and effluent of the REMOX <br /> incinerator. Influent samples were obtained on January 20 , May <br /> 21, June 22, July 15, August 26, September 9 and September 11, <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. Prior to sampling the wells or the system, a <br /> calibrant prepared from fresh gasoline is infected into the GC- <br /> PID. The resulting chromatogram has numerous responses. The <br /> microprocessor of the GC-PID computes the area per response in <br /> volt seconds and assigns a peak # and retention time. The sum of <br /> all the responses are then used to obtain a mg/L per volt second <br /> calibrant factor, which is used to calculate mg/L as gasoline <br /> vapor from each analysis produced. Pounds per day can be <br /> computed using these mg/L values produced from the analysis of the <br /> different vapor recovery wells, the influent to the oxidizer, the <br /> pressure differential created at the orifice to determine flow <br /> rates for each well, and the influent to the oxidizer. The pounds <br /> • per day values for each well and the influent are averaged with <br /> the preceding site visit ' s pound per day value. This figure is <br /> then multiplied by the number of days the system operated between <br /> visits to estimate the total pounds each well and the system has <br /> removed for that time period. This poundage is added to the <br /> accumulated poundage of the previous visit to update the total <br /> pounds removed to date. The effluent sample is computed in the <br /> same fashion, but also includes natural gas flow along with the <br /> 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 f itted <br /> polytubing. The sample port is then opened and the syringe is <br /> purged by pulling and pushing the syringe plunger several times <br /> filling and depleting the syringe of that particular well ' s vapor <br /> stream. Then the syringe is filled, the sample valve is closed, <br /> and forceps are used to clamp onto the soft polytubing to create <br /> an air tight seal for the syringe before removing the syringe from <br /> the sample port. Once the 60 cc syringe is removed with the <br /> rl amparl pn7 y+i�hing atta�}:�d, the pluiger is pusaied into the <br /> syringe to create pressure within the syringe and released to <br /> allow the vapors that have been captured to reach equilibrium. A <br /> small dedicated needle attached to a dedicated 1 cc syringe is <br /> then inserted into the 60 cc syringe via the soft tubing for <br /> PAGE 6 <br />
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