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2900 - Site Mitigation Program
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PR0536777
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Last modified
6/18/2019 11:24:32 AM
Creation date
6/18/2019 11:08:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0536777
PE
2960
FACILITY_ID
FA0021126
FACILITY_NAME
FORMER COUNTRYSIDE MARKET
STREET_NUMBER
10848
STREET_NAME
COPPEROPOLIS
STREET_TYPE
RD
City
STOCKTON
Zip
95215
APN
10311006
CURRENT_STATUS
01
SITE_LOCATION
10848 COPPEROPOLIS RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Therefore,in consultation with Mr. Sasson, H&A terminated the inv stigation and <br /> directed the backhoe operator to obtain a scoop of fresh soil from tht floor of the <br /> excavation. After Upgradient Environmental collected a sample fron i the bucket, the <br /> backhoe filled the excavation with imported pea gravel and the exca ated soil was <br /> transported to REMCO in Richmond, California for treatment. Sample CM-1-13' was <br /> transported to Sequoia Analytical and analyzed for Total Petroleum Hydrocarbons as <br /> gasoline (TPH-g) and benzene, toluene, ethylbenzene, and xylene (BTEX). The <br /> laboratory reported weathered gasoline in the C6-C12 range, with all analytes present <br /> except benzene (Table 1). Upgradient Environmental submitted a report of the - <br /> investigation to PHS/EHD the following month.No further work was requested by <br /> Stockton Mortgage or H&A. <br /> Sometime after 1995, San Joaquin County obtained the property frot a the trusts that had <br /> held the first mortgage. Recently, the County offered the property in an auction sale and <br /> it was purchased by Mr. Henry. <br /> 3.0 PROCEDURES <br /> The planned scope of-work was to drill one boring to an estimated d pth of 50 feet <br /> through the former tank cavity to determine the maximum vertical e tent of soil <br /> contamination, and three borings in a triangular pattern around it to ssess the lateral <br /> extent of contamination, including one boring to 80 feet to collect a vater sample. <br /> However, this plan was altered while drilling the first boring(CM1)through the tank <br /> cavity. Soil samples collected from this boring indicated that hydroc irbons were still <br /> present at high concentrations at 50 feet, so the driller was instructed to continue drilling <br /> until the lower limit of contamination was reached. This occurred at the approximate <br /> depth of the static groundwater level (90 feet), and'a water sample was collected. This <br /> made it possible to eliminate the deep boring east of the tank cavity, and also provided an <br /> indication of the magnitude of the problem. Therefore, only one add tional boring was <br /> drilled. Boring CM2 was drilled 25 feet south of the excavation(Fig e 2).This is 10 feet <br /> farther south than planned. The location was moved because the,big organic vapor <br /> readings obtained from CM 1,samples suggested that the extent of c ntamination might be <br /> greater than originally anticipated. <br /> V&W Drilling of Rio Vista, California used a Mobile Drill B-61 ho low-stem auger rig to <br /> drill the borings. Soil samples were collected at 5-foot intervals, beE inning at a depth of <br /> 15 feet in CMI and 10 feet in CM2. The samples were screened for he presence of <br /> organic vapors with a portable photo-ionization detector(PID), pres rved in a cooled ice <br /> chest for later laboratory analysis, and described on the boring log( ppendix A). A <br /> disposable plastic bailer was lowered through the augers to collect a water sample before <br /> CMl was abandoned. Both borings were backfilled by pumping cement-bentonite grout <br /> through a tremmie pipe. Drill cuttings were stored on plastic sheeting near the eastern <br /> property line. <br /> Twelve soil samples and the water sample were shipped to McCain bell Analytical <br /> Laboratory in Pacheco,where they were analyzed for TPH-g, MTB (methyl tertiary <br /> 3 <br />
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