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ARCHIVED REPORTS XR0006466
EnvironmentalHealth
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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 /> obtaining the sample to be in3ected into the PID-GC. Again the <br /> lcc syringe is purged numerous times prior to filling it with the <br /> sample. All but 0 . 5 cc of the sample is ejected into the air <br /> prior to infecting the remaining 0 . 5 cc syringe sample into the <br /> GC-PID (the calibrant injection is 0 . 5 cc) . Once the chromatogram <br /> has been recorded an instrument blank is run prior to the next <br /> sample. The instrument blank will indicate if residual peaks are <br /> being carried onto the next analysis. <br /> While the GC-PID analysis is running for a particular sample ( 15 <br /> minutes per sample run) , vacuum influent readings are obtained <br /> from the wells by attaching a manometer calibrated in mm water to <br /> sample ports at the well heads. These readings show the mm water <br /> pressure or vacuum that is being created at each well. <br /> Occasionally the 10550 PID-GC is not available for field <br /> determination of the influent and effluent streams. Tedlar bag <br /> samples are then obtained and brought back to the WEGE portable <br /> laboratory for analysis using a FID-GC, see Appendix C - Field <br /> Notes. <br /> VAPOR RECOVERY OPERATIONS AND RESULTS <br /> As has been stated in earlier reports, soil contamination exists <br /> from beneath the tank excavation to the top of the ground water, <br /> see Fence Diagram Figure 6 . Overexcavatx.on during the initial tank <br /> removal, removed contaminated soil to the 25 foot depth. Prior <br /> to replacement of the new double contained fiberglass tanks and <br /> dispensing system, 4 inch and 6 inch SCH 40 PVC 0 . 02 inch slotted <br /> pipes were placed vertically at the north corner and west corner <br /> of the excavation respectively and manifolded via underground to <br /> the treatment compound with SCH 40 2 inch and 4 inch PVC pipe. <br /> These pipes along with monitor wells MW1, MW2 , MW3 and MW10 are <br /> being used for vapor extraction - soil and ground water <br /> remediazzon. <br /> On October 10 , 1991 the vapor extraction system operated for 6 <br /> hours, to check the auto shut downs and percent destruction of the <br /> REMOX unit, using monitor wells MW1, MW10, and the excavation <br /> wells. The system was restarted on. October 11 , 1991 for the <br /> initial inspection and operation of the system. The unit operated <br /> until November 5 , 1991 , when it was shut down to replace a worn <br /> bearing. The system was restarted after the repairs on November <br /> 20, 1991 and operated until December 24, 1991. On this date <br /> SviTieOite turned vll 1.11G liialil Lrean.at l.11a4 SGr'v.1.Ce7 l,1iC t1Cal.111C114 <br /> compound. This breaker box has since been locked. The unit was <br /> restarted on January 3 , 1992 and operated until July 20 , 1992, <br />. with occasional auto shut downs due to high temperature ( 15500F) <br /> in the pre-oxidation chamber. On July 20 , 1992, the heat <br /> PAGE 7 <br />
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