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ARCHIVED REPORTS XR0006541
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0006541
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Last modified
8/21/2019 3:47:34 PM
Creation date
8/21/2019 3:09:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006541
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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R603 UPDATE-14 3/25/93 <br /> 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 <br /> retention times in the above chromatograph, DCE = 2 . 079 minutes, <br /> TCE = 3 . 023 minutes and PCE = 3 . 75 minutes . Before sampling the <br /> wells or the system, a calibrant made from fresh gasoline is <br /> in3ected into the GC-PID and GC-FID. The resulting chromatograms <br /> has numerous responses The microprocessor of the GC-PID and GC- <br /> FID computes the area per response in volt seconds and assigns a <br /> peak number and retention time The sum of all the responses are <br /> then used to obtain a mg/L per volt second calibrant factor, <br /> which is used to calculate mg/L as gasoline vapor from each <br /> analysis produced. Pounds per day can be computed using these <br /> mg/L values produced from the analysis of the different vapor <br /> recovery wells, the influent to the oxidizer, the pressure <br /> differential created at the orifice to determine flow rates for <br /> each well, and the influent to the oxidizer The pounds per day <br /> values for each well and the influent are averaged with the <br /> preceding site visit' s pound per day value . This figure is then <br /> multiplied by the number of hours the system operated between <br /> visits , to estimate the total pounds each well and the system has <br /> removed for that time period This figure is added to the <br /> accumulated poundage of the previous visit to update the total <br /> pounds removed. The effluent sample is computed in the same <br /> 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 /> poly tubing to a sample port on the vapor recovery manifold (on <br /> the well side of the orifice plate) . The tubing is attached to a <br /> air tight fitting that connects a valved one liter tedlar bag <br /> which is placed inside a air tight sample box. The sample port <br /> is opened and a vacuum is placed on the tedlar bag inside the <br /> sample box, filling the tedlar bag with the vapor stream Once <br /> full the sample port is closed, the vacuum is withdrawn and the <br /> tedlar bag valve is closed, sealing the vapor stream sample <br /> inside the tedlar bag A small dedicated needle attached to a <br /> dedicated 1 cc syringe is then inserted into the septum of the <br /> tedlar bag to obtain the sample to be in3ected into the PID-GC <br /> and FID-GC The 1cc syringe is purged numerous times before <br /> filling it with the sample All but 0 5 cc of the sample is <br /> elected into the air before injecting the remaining 0 . 5 cc <br /> syringe sample into the chromatographs (the calibrant in3ection <br /> is 0 . 5 cc) Once the chromatogram is recorded an instrument <br /> blank is run prior to the next sample. The instrument blank <br /> indicates if residual peaks are being carried onto the next <br /> analysis . <br /> Prior to sampling an individual vapor stream, flow rates are <br /> recorded and vacuum influent readings are obtained from the wells <br /> by attaching a manometer calibrated in mm water to sample ports <br /> PAGE 6 <br />
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