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ARCHIVED REPORTS XR0005957
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544590
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ARCHIVED REPORTS XR0005957
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Last modified
6/21/2019 1:58:28 PM
Creation date
6/21/2019 11:02:55 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005957
RECORD_ID
PR0544590
PE
3528
FACILITY_ID
FA0003932
FACILITY_NAME
KWIKEE FOODS
STREET_NUMBER
2081
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
APN
12315225
CURRENT_STATUS
02
SITE_LOCATION
2081 COUNTRY CLUB BLVD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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r <br /> 3.2 Phase 2—Extent of Contaminated Soil <br /> In July 1997, PHS/EHD held a meeting at the County office with Mr. Peters and requested him to <br /> submit a new work plan to continue the assessment of the contamination. On behalf of Mr. Peters, <br /> Upgradient Environmental submitted a work plan to drill five borings, including four monitor <br /> wells, in the second phase of assessment. This plan was amended in February 1998 and again in <br /> April 1998, as a result of information obtained when the two underground storage tanks were <br /> removed from the site. In the April amendment, the objective of the second phase was changed <br /> from an assessment of soil and groundwater contamination to a more limited assessment of soil <br /> contamination. <br /> 3.2.1 Tank Removal Results <br /> The 10,000-gallon tanks were removed by SEMCO, Inc., and Upgradient Environmental witnessed <br /> the removal and prepared the Tank Removal Report(March 30, 1998). The tanks were not replaced, <br /> and the tenants of the property ceased selling gasoline at that time. <br /> Although neither tank was excessively rusted nor damaged, four holes were found, one in each end <br /> of both tanks. The sandy backfill material near the ends of the tanks was badly discolored with <br /> petroleum, but the native clay beneath the backfill material appeared to be only slightly stained and <br /> relatively uncontaminated. Soil samples collected from the clay at the ends of the tanks confirmed <br /> the visual observations: petroleum hydrocarbons were present at low to moderate concentrations in <br /> all four samples from the base of the excavation and at low concentrations in the six samples from <br /> the excavated soil (Table 4). In addition, because groundwater entered the excavation during the <br /> removal and a (gasoline) sheen was apparent on the surface of the standing water, a bailer was <br /> lowered into the excavation and two water samples were collected. Hydrocarbons were detected in <br /> both samples at concentrations that considerably exceeded those found in the monitoring wells. The <br /> evidence of soil contamination around the tanks led to focusing the second phase of drilling on <br /> determining the extent of soil contamination. <br /> 3.2.2 Installation of Soil Borings <br /> In the second phase, five borings were drilled around the perimeter of the former tank cavity and <br /> soil samples were collected at variable intervals, generally starting near the base of the former tank <br /> cavity (15 feet). The borings were drilled with a truck-mounted Geoprobe® rig, and were not <br /> converted into monitoring wells. The soil' samples were analyzed for TPH-g, BTEX, gasoline <br /> oxygenates (including methanol at the request of PHS/EHD), total organic carbon (TOC), bacterial <br /> abundance, hydraulic conductivity, and porosity. <br /> The results of this phase of investigation were reported in the First Quarter 1998 Report (M�ty 30, <br /> 1998). Fourteen soil samples were analyzed, ranging in depth from 15 to 36 feet (Table 2). The <br /> results were quite similar to those obtained from the first phase of drilling: minimal evidence of soil <br /> contamination, mostly in the form of benzene. A hydrocarbon isocontour map was prepared (Figure <br /> 3 <br />
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