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ARCHIVED REPORTS XR0006468
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0006468
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Last modified
8/21/2019 3:56:46 PM
Creation date
8/21/2019 2:54:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006468
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-9 9/14/92 <br /> • <br /> The sample port is then opened and the syringe is purged by <br /> pulling and pushing the syringe plunger several times filling and <br /> depleting the syringe of that particular wells vapor stream. Then <br /> the syringe is filled, the sample valve closed and forceps are <br /> used to clamp onto the soft polytubing to create an air tight seal <br /> for the syringe before removing the syringe from the sample port. <br /> Once the 60 cc syringe is removed with the forceps clamped <br /> polytubing attached, the plunger is pushed into the syringe to <br /> create pressure within the syringe and released to allow the <br /> vapors that have been captured to reach equilibrium. A small <br /> dedicated needle attached to a dedicated 1 cc suringe is then <br /> inserted into the 60 cc syringe via the soft tubing for obtaining <br /> the sample to be injected into the PID-GC. Again the lcc syringe <br /> is purged numerous times prior to filling it with the sample. All <br /> but 0 . 5 cc of the sample is ejected into the air prior to <br /> injecting the remaining 0 .5 cc syringe sample into the GC--PID (the <br /> calibrant injection is 0 . 5 cc ) . Once the chromatogram has been <br /> recorded an instrument blank is run prior to the next sample. The <br /> instrument blank will indicate if residual peaks are being carried <br /> 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 /> ii Occasionally the lOS50 PID-GC is not available for field <br /> determination of the influent and effluent streams . Tedlar bag <br /> it 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 /> j 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 /> Overexcavation during the intial tank removal , removed <br /> contaminated soil to the 25 foot depth. Prior to replacement of <br /> the new double contained fiberglass tanks and dispensing system, 4 <br /> inch and 6 inch SCH 40 PVC 0 . 02 inch slotted pipes were placed <br /> vertically at the north corner and west corner of the excavation <br /> respectively and manifolded via underground to the treatment <br /> i compound with SCH 40 2 inch and 4 inch PVC pipe . These pipes <br /> along with monitor wells MW1 , MW2 , MW3 and MW10 are being used for <br /> vapor extraction - soil and ground water remediation. <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 /> i <br /> PAGE 7 <br /> i <br />
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