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ARCHIVED REPORTS_XR0003256
Environmental Health - Public
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PR0545289
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ARCHIVED REPORTS_XR0003256
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Last modified
2/11/2020 10:02:19 PM
Creation date
2/11/2020 8:43:21 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003256
RECORD_ID
PR0545289
PE
3528
FACILITY_ID
FA0003828
FACILITY_NAME
VAN BUSKIRK GOLF COURSE
STREET_NUMBER
1740
STREET_NAME
HOUSTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
APN
16307036
CURRENT_STATUS
02
SITE_LOCATION
1740 HOUSTON AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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City of Stockton A68101.02C <br /> February 23, 1996 Page 8 <br /> dispenser location. Likewise, soil sample location SB-4 is proposed to delimit the extent of <br /> PPC migration on the southwest side of the former fuel dispenser location. <br /> Analytical results for the soil sample collected from the north wall of the former excavation <br /> detected the highest concentrations of TPH-G and benzene, toluene, ethylbenzene, and <br /> xylenes (BTEX). The purpose of sample location SB-5 is to delimit the northward extent <br /> of PPC migration. <br /> The purpose of soil sample location SB-6 is to investigate the possibility of gasoline <br /> constituents in the vicinity of the former gasoline UST. This location will also delimit the <br /> northwestward extent of PPC migration from the former diesel UST location. <br /> In the event field screening (as outlined in Section "4.1.3 Soil Sampling Technique") <br /> indicate the presence of PPCs in the subsurface soil at any of the sampling locations, more <br /> data will be need to delimit the migration of PPCs. Contingency soil sample locations would <br /> be used to further investigate PPC migration in the soil. These contingency soil sample <br /> locations would be "stepped out" away from the presumed source in logical increments in <br /> an attempt to develop additional data for PPC concentration attenuation and to delimit the <br /> extent of PPC migration in soil. <br /> . 4.1.2 Soil Sample Depths: Prior to collecting soil samples, the on-site monitoring wells will <br /> be sounded to determine the depth of groundwater beneath the site. Soil samples will not <br /> be collected from a depth which is greater than the groundwater depth. One sample will <br /> be collected at approximately 10 feet BSG at each sampling location. A second sample will <br /> be collected from approximately 1 foot above the measured groundwater depth at each <br /> sampling location. <br /> 4.1.3 Soil Sampling Technique: The soil samples will be collected from boreholes drilled <br /> to the sample depths using a 1.5-inch diameter, solid flight, portable power auger. Upon <br /> drilling to the sample depth, the power auger will be removed from the borehole for soil <br /> sample collection. Auger cuttings will be field screened using a photoionization detector <br /> (PID) consistent with our SOPS for evidence of PPCs and for the purpose of preparing <br /> lithologic logs. The auger flights will be decontaminated after completion of each borehole. <br /> Soil samples will be collected with a 1.5-inch diameter soil sampler equipped with a 6-inch <br /> long stainless-steel sample sleeve. The sampler will be driven into the undisturbed soil at <br /> the bottom of the borehole. After recovering the sampler, the sleeve will be labeled and <br /> preserved consistent with our SOPs for delivery to the chemical laboratory.The sampler will <br /> be decontaminated after collecting each sample. <br /> Soil samples will be submitted for laboratory testing consistent with the analytical methods <br /> outlined in Section " 4.3 Laboratoa Testing Pro am". The analytical results of soil <br /> i! samples collected are expected to provide data on PPC concentrations in subsurface soil. <br /> This data will be used to evaluate the lateral extent of PPC migration in soil. <br />
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