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ARCHIVED REPORTS XR0006490
Environmental Health - Public
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EHD Program Facility Records by Street Name
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P
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PACIFIC
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6425
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2900 - Site Mitigation Program
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PR0519189
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ARCHIVED REPORTS XR0006490
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Last modified
8/21/2019 4:26:36 PM
Creation date
8/21/2019 2:58:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006490
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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REG 603 UPDATE-6 2/21/92 <br /> • <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 /> 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 /> 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 forcepts are <br /> used to clamped onto the soft polytubing to create an air tight <br /> seal for the syringe before removing the syringe from the sample <br /> . port. 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 effected into the air prior to <br /> infecting the remaining 0. 5 cc syringe sample into the GC-PID (the <br /> calibrant infection 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 zhe 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 /> samnle ports at the well heads_ These readings show the mm water <br /> pressure or vacuum that is being created at each well. <br /> VAPOR RECOVERY OPERATIONS AND RESULTS <br /> As has been stated above, soil contamination exists from beneath <br /> the tank excavation to the top of the ground water. <br /> Overexcavation during the intaal 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 /> PAGE 9 <br />
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