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ARCHIVED REPORTS_XR0002123
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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HAMMER
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3500 - Local Oversight Program
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PR0544983
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ARCHIVED REPORTS_XR0002123
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Last modified
11/15/2019 8:33:26 AM
Creation date
11/15/2019 8:19:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002123
RECORD_ID
PR0544983
PE
3528
FACILITY_ID
FA0005197
FACILITY_NAME
GARYS EXXON SERVICE STATION
STREET_NUMBER
909
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
CURRENT_STATUS
02
SITE_LOCATION
909 W HAMMER LN
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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r <br /> 2 <br /> r <br /> • <br /> r <br /> The temporary vapor probes installed for the investigation <br />' were constructed of 1/2-inch diameter Schedule 40 steel <br /> pipe. A point was forged on one end. A 24-inch range of <br /> 3/16-inch perforations were drilled into the probe beginning <br />' at 3 inches from the point (Figure A) . The vapor probes <br /> were driven pneumatically into the soil at various depth <br /> intervals. The depth intervals include 8 to 10 feet, 14 to <br /> 16 feet, 19 to 21 feet, 28 to 30 feet, and 32 to 34 feet <br /> below grade. In locations where the soil was covered by <br /> concrete or asphalt, a 1-inch diameter hole was drilled <br /> through the surface material with an electric roto-hammer. <br /> I The existing groundwater monitoring wells were screened at a <br /> depth interval of 28 to 58 feet below grade. <br /> After installation, a vacuum was applied to each probe to <br /> extract soil. gas. One psi sample pressure was maintained <br /> during the analysis. Sample flow rate and instrument <br /> pressures were checked before each test. The soil gas was <br /> sampled through a 1/4-inch Teflon sample line that was <br /> connected to a stainless steel well head fitting. Use of <br /> Teflon tubing minimizes sample loss through adsorption and <br /> the possibility of distorted results from a sample line <br /> contaminated by a previous analysis. Leak checks were <br /> performed on the sample line before and during the analysis. <br /> I Filters were used extensively throughout the system to <br /> remove foreign material from the sample pathway. The sample <br /> line was connected to a diaphragm pump located in a mobile <br /> laboratory. The extracted soil gas was analyzed using a <br /> Beckman Model 400 Total Hydrocarbon Analyzer equipped with a <br /> Flame Ionization Detector (FID) and the results recorded on <br /> a Houston Instruments chart recorder. The Beckman Model 400 <br /> was calibrated using certified standards of propane in <br /> nitrogen. The instrument was recalibrated periodically <br /> throughout the day using certified standards. <br /> Performance Test <br /> A portable skid containing a vacuum pump, flow meters, and <br /> vacuum gauges was used on site. A rigid vacuum line was <br /> connected to a probe or monitoring well to create an <br /> extraction point. Three of the temporary vapor probes <br /> r installed for the Soil Gas Survey and three existing <br /> i monitoring wells were used as extraction points. A set <br /> volume of air was pumped from the extraction point. Each <br /> Iextraction point was tested for a maximum of 15 minutes. <br /> . The information from the Performance Test was used to <br /> determine the capture radius, the distance at which the <br /> i <br />
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