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ARCHIVED REPORTS XR0006469
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0006469
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Last modified
8/21/2019 4:00:51 PM
Creation date
8/21/2019 2:55:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006469
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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REG 603 UPDATE-8 7/17/92 <br /> • <br /> prior to a filter in front of the vacuum pump After the vapor <br /> stream leaves the vacuum pump, it .is pushed into the thermal <br /> oxidizer (RXL 400) which oxidizes the gasoline range hydrocarbon <br /> vapors at no less than 14000F and no greater than 15500F. <br /> Influent samples are obtained from the exit of the pump and <br /> effluent samples are obtained from the stack of the thermal <br /> oxidizer. The gasoline range hydrocarbons are oxidized into heat, <br /> CO2 and water vapor, see UPDATE STATUS REPORT #5. <br /> A portable ambient air PID-GC (Photovac 10550 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 October 22, and 24, 1991, "Tedlar" bag <br /> samples were obtained of the influent and effluent of the REMOX <br /> incenerator and on January 20, May 21, and June 22, 1992, a <br /> influent sample was obtained. These samples were analyzed for TFH <br /> and BTEX along with screening for Tetrachloroethylene (PCE) , <br /> Trichloroethylene (TCE) and 1,2,-Dichloroethane (DCE) using a <br /> Shimadzu GC-FID chromatograph mounted permanently in WEGE's <br /> portable laboratory These compounds have the following retention <br /> times in the above chromatograph, DCE = 2.079 minutes, TCE = 3.023 <br /> . minutes and PCE = 3 75 minutes. Prior to sampling the wells or <br /> the system, a cal.ibrant prepared from fresh gasoline is infected <br /> into the GC-PID. The resulting chromatogram has numerous <br /> responses. The microprocessor of the GC-PTD computes the area, <br /> per response, in volt seconds, and assigns a peak #, and retention <br /> time The sum of all the responses are then used to obtain a mg/L <br /> per volt second calibrant factor, which is used to calculate mg/L <br /> as gasoline vapor from each analysis produced. Using these mg/L <br /> values produced from the anlaysis of the different vapor recovery <br /> wells and the influent to the oxidizer, and the pressure <br /> differential created at the orifice to determine flow rates for <br /> each well and the influent to the oxidizer, pounds per day can be <br /> computed. The pounds per day values for each well and the <br /> influent are then averaged to the preceeding site visits pound per <br /> day and then multiplied by the number of days the system operated <br /> between visits to estimate the total pounds each well and the <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 The effluent sample is computed <br /> in the same fashion, but also includes natural gas flow along with <br /> the influent orifice flow rate. <br /> C 2 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, <br /> well side of the orifice plate, with air tight fitted polytubing <br /> . The sample port is then opened and the syringe is purged by <br /> PAGE 8 <br />
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