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Last modified
1/24/2020 4:49:57 PM
Creation date
1/24/2020 4:38:23 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0545210
PE
3528
FACILITY_ID
FA0004548
FACILITY_NAME
WALMART #2025
STREET_NUMBER
3010
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
238-020-15
CURRENT_STATUS
02
SITE_LOCATION
3010 W GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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.i <br /> r <br /> Mr. Ron Rowe i <br /> July 26, 2000 <br /> Page Four <br /> SOIL ASSESSMENT <br /> Four soil borings were placed at the site utilizing a direct push drill rig. Prior to drilling, <br /> Underground Service,Alert was notified. One boring was placed adjacent to the former tank <br /> excavation. The remaining borings were placed approximately fifteen from the former UST <br /> excavation. Two borings were placed downgradient to the former tank excavation and one boring <br /> was placed upgradient; based on surface topography. The location of the borings is illustrated in } <br /> Figure 2. The soil borings were advanced until the first encounter of saturated soils. Soil samples <br /> were collected continuously throughout the boring. ,:Soil samples were obtained from the boring # <br /> using a 1.5 inch inside diameter(11)),45 inch long,nickel plated core barrel sampler attached to the <br /> end of the boring rods. Soil samples were collected by pushing the barrel sampler through the E <br /> desired sampling depth with the direct push drill;rig. The sampler was recovered with a section of } <br /> undisturbed soil collected within the acetate liner inside the core barrel. A section of undisturbed <br /> soil from each four feet liner was capped with teflon and plastic end caps and placed..on ice for � <br /> preservation,pending possible laboratory analysis. The remaining portion of soil was subjected to <br /> headspace analysis in'-the field utilizing an organic'.vapor monitor (OVM). Soil lithology was <br /> recorded in the field and each sample was inspected for evidence of staining, odors and other signs <br /> of contamination. Two soil samples per boring were submitted for chemical analysis. <br /> Soil samples were sent via over-night courier to a certified laboratory for chemical analyses. Soil <br /> samples were analyzed for total petroleum hydrocarbons-gasoline range(TPH-G 8015/2020);TPH <br /> - diesel range (TPH-D 8015); benzene, toluene, ethylbenzene, and xylene (BTEX 801518020), <br /> methyl-t-butyl ether (MTBE 8260), ethyl-t-butylether(ETBE 8260), methyl-t-amyl ether (TAME <br /> 8260), and isopropylether(DIPE 8260). <br /> I <br /> SOIL CONDITIONS <br /> Soil samples were collected continuously throughout each soil boring to a depth of sixteen feet <br /> below ground surface(bgs). Generally,soil samples were collected near the base of the former UST <br /> and at the base of the soil boring at the soil/groundwater interface. Soil samples were screened on- <br /> site utilizing an OVM The soil samples did not display detectable organic vapor readings. No <br /> evidence of staining, odors, or other signs of contamination were observed. Soil in the vicinity of <br /> the former UST consisted of very stiff gray clay to a depth of four feet. Light brown, medium stiff <br /> clay and silt was encountered to total depth. Groundwater was encountered at a depth of 16 feet. <br /> Groundwater did not display odors or sheening. 'Soil boring logs are provided in Attachment C. <br /> i <br /> i <br /> ANALYTICAL RESULTS <br /> Eight soil samples were submitted to Test America, Inc. located in Nashville, Tennessee for <br /> laboratory analyses. Test America is a state of California certified laboratory. Eight soil samples <br /> were analyzed for TPH=G,TPH-D,BTEX,MTBE,ETBE,TAME,and DIPE. Only one soil sample <br /> revealed detectable target constituent concentrations. One soil sample collected from soil boring SB- <br /> 3 at a depth of 15.5 - 16 feet (SB-3, 15.5 - 16 ft) contained xylenes at a concentration of 0.0039 <br /> mg/kg, slightly above the laboratory detection limit of 0.0020 mg/kg. A summary of the soil <br /> analytical results are provided in Table 3. A copy of the laboratory analytical report is included in <br /> Attachment D. <br /> 00268115.2.85 " <br />
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