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3500 - Local Oversight Program
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PR0544990
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Last modified
11/15/2019 1:56:13 PM
Creation date
11/15/2019 1:47:42 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0544990
PE
3528
FACILITY_ID
FA0006902
FACILITY_NAME
TRACY WASTEWATER TX PLNT
STREET_NUMBER
3900
STREET_NAME
HOLLY
STREET_TYPE
DR
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
3900 HOLLY DR
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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All drilling equipment and sampling tools were cleaned prior to arriving, and before leaving the <br /> site. The probe was advanced collecting continuous cores of soil in borehole B-1 and interval <br /> sampling in the remaining boreholes. The sampler was retrieved and dissembled, and the soil <br /> filled acetate liner was sealed with Teflon paper or foil and plastic endcaps, labeled, logged onto <br /> chain-of-custody forms and place in a chilled ice chest on crushed ice. Soil sample intervals <br /> retained for chemical analysis were cut from the liners at depths of suspected contaminant <br /> presence. <br /> The boreholes were logged using the Unified Soil Classification System under the supervision of <br /> a registered geologist. Additional lithologic information was collected to describe the subsurface <br /> geology. Soil samples were field screened for petroleum soil vapor using a photoionization <br /> vapor meter calibrated to the manufacturers specifications. Interval samples were collected at <br /> five-foot intervals, at intervals of obvious contamination and at stratigraphic features of interest. <br /> Upon completion of the borehole drilling and collection of water samples, all boreholes were <br /> backfilled with grout, placed from the bottom to top of the borehole and a PHS EHD <br /> representative witnessed the process. <br /> Groundwater Sampling <br /> Each exploratory boring was sampled. The ground water samples collected from the boreholes <br /> was used for a reconnaissance of the site groundwater contamination. A brief summary of these <br /> procedures follows: Each borehole was advanced into the aquifer and temporarily cased for <br /> sampling. Depth to groundwater measurements were made to the nearest one-one hundredth of <br /> one foot, and also checked for the presence of separate phase product. The water entering the <br /> borehole was sampled using a clean bailer, and carefully poured into the appropriate laboratory <br /> prepared container with minimum cavitation. Each water sample was labeled, logged onto a <br /> chain-of-custody form, and placed in a chilled ice chest for transport to the laboratory. <br /> Subsurface Conditions <br /> Four borings were advanced on the site. The borings revealed silty clay to depths of about nine <br /> to 15 feet. Boring B-4 was drilled through the former tank pit and revealed silty gravel backfill <br /> to a depth of nine feet and underlain by sandy clay to a depth of 14 feet. The clay strata are <br /> underlain by sandy silt, clayey sand and sand to depths of about 16 to 20 feet, and appear to grade <br /> laterally with each other. A clay stratum underlies the sandy strata. The clayey stratum appears <br /> laterally continuous in the general area of the site investigation(see Figure 1). <br /> Groundwater occurs at depths of 13 to 14 feet and initially stabilized in uncased boreholes at <br /> depths of 8.7 to 11.9 feet. Groundwater appears to be unconfined to slightly confined however <br /> boreholes were not open long enough to allow for 24 hours of stabilization for additional <br /> groundwater measurements. <br /> Page 2 of 6 <br />
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