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ARCHIVED REPORTS_XR0005524
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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N
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99 (STATE ROUTE 99)
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24323
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3500 - Local Oversight Program
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PR0544358
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ARCHIVED REPORTS_XR0005524
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Last modified
11/19/2024 1:50:25 PM
Creation date
4/17/2019 3:13:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005524
RECORD_ID
PR0544358
PE
3528
FACILITY_ID
FA0021623
FACILITY_NAME
JAHANT FOOD AND FUEL
STREET_NUMBER
24323
Direction
N
STREET_NAME
STATE ROUTE 99
City
ACAMPO
Zip
95220
APN
00516019
CURRENT_STATUS
02
SITE_LOCATION
24323 N HWY 99
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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The single soil boring will be drilled to a depth of approximately 90 feet bgs The final total depth of <br /> the soil boring will be approximately five feet below the depth of the first encountered groundwater- <br /> bearing zone The boring will be advanced with a truck-mounted drill ng using 8-inch outside- <br /> diameter hollow stem augers Soil samples will be collected at five-foot intervals using a modified <br /> California split spoon sampler, lined with two-inch diameter brass sleeves A field geologist will log <br /> all soil samples for hydrogeologic and lithologic characteristics according to the Unified Soil <br /> Classification System and screen each sample for any hydrocarbon vapors using an organic vapor <br /> monitor, equipped with a photolonization detector (PID) Based on the PID measurements, up to <br /> six soil samples will be seated with Teflon® paper and plastic end caps, labeled and transported in <br /> an iced cooler under chain-of-custody documentation to a state of California certified hazardous <br /> waste testing laboratory Prior to soil sample submission to the laboratory, PHSIEHD will be <br /> consulted <br /> Upon encountering saturated soil and groundwater in the soil boring, the boring will be advanced <br /> an additional five feet into the saturated zone To collect a groundwater-grab sample, a two-inch <br /> diameter polyvinyl chloride (PVC) temporary well will be constructed and installed in the borehole <br /> The temporary well will consist of 10 feet of flush-threaded and machine-slotted (0 020-inch) well <br /> screen spanning approximately five feet above and five feet below the static groundwater level <br /> Blank PVC casing will thread into the top of the well screen and extend to the surface Neither a <br /> sand pack nor a well seal will be installed in the temporary well <br /> Prior to groundwater-grab sampling, the temporary well will be purged of approximately three well <br /> volumes using a weighted, dedicated and disposable bailer During purging, groundwater <br /> temperature, pH and electrical conductivity will be recorded Once the groundwater in the <br />' temporary well is purged and recharged to at least 90% of its original groundwater column <br /> thickness, a groundwater-grab sample will be collected The groundwater-grab sample will be <br /> collected with the disposal bailer and poured into laboratory-supplied containers The containers <br /> will be labeled and transported in an iced cooler under chain-of-custody documentation to a state of <br /> California certified hazardous waste testing laboratory <br /> Once the soil and groundwater-grab sampling is completed, the temporary well will be removed and <br /> the sod boring will be abandoned with 20 1 cement bentonite grout, installed to the bottom of the <br /> borehole using a tremae pipe Following borehole abandonment, the surface composition will be <br /> restored Waste soil generated during the drilling of the soil boring will be stockpiled at the site <br /> using a base and cover of plastic sheeting Proper disposition of the waste sod will be based on the <br /> results of the sod sample analyses Equipment nnsate water and purged groundwater will be <br /> stored on-site in 55-gallon drums pending waste profiling and proper disposition <br /> 8 <br />
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