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ARCHIVED REPORTS_XR0008376
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0541936
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ARCHIVED REPORTS_XR0008376
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Entry Properties
Last modified
5/18/2020 11:45:25 AM
Creation date
5/18/2020 11:27:08 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008376
RECORD_ID
PR0541936
PE
2957
FACILITY_ID
FA0006149
FACILITY_NAME
RANCH MARKET
STREET_NUMBER
23569
Direction
S
STREET_NAME
SANTA FE
STREET_TYPE
RD
City
RIVERBANK
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
23569 S SANTA FE RD
QC Status
Approved
Scanner
LSauers
Tags
EHD - Public
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1 Problem Assessment Report Page 6 <br /> Ranch Market,23569 South Santa Fe Road,Riverbank,CA November&,2000 <br /> characterization The auger steam cleaning water was retained and stored in one 55-gallon <br /> drum pending offsite disposal <br /> 4.2 Soil Sampling <br />' Soil samples were collected from four of the seven borings and at 5-foot Intervals, beginning <br /> at various depths as described above Samples were collected from the HSA borings using a <br /> 2 5-Inch O D split-spoon sampler, lined with three 2-inch-diameter by 6-inch-long brass <br />' sample tubes The split-spoon sampler was driven 18 inches ahead of the augers at each <br /> sample point Selected soil samples were field screened for hydrocarbon vapors using a PID <br /> Working under the supervision of a California registered geologist, SECOR's field geologist <br /> logged the soil samples using the Unified Soil Classification System (Appendix B) Copies of <br /> the field notes detailing the well installation are included in Appendix C <br />' Selected samples were sealed, labeled and placed on ice in an insulated container for transport <br /> under chain-of-custody manifest to Kiff Analytical LLC, a California state-certified analytical <br /> laboratory located in Davis, CA <br />' Soil samples submitted for laboratory analysis were chosen on the basis of PID readings, <br /> P rY Y 8 <br />' lithology, historical analytical results, and depth to groundwater observed in each boring <br /> Selected samples were analyzed using U S Environmental Protection Agency (EPA) method <br /> 8260B for BTEX, TPHg, and MtBE <br /> 10 4.3 Air Sparge and Soil Vapor Extraction Well Installation <br />' One air sparge well was installed in boring AS-1 using 2-inch-diameter, schedule 40 PVC <br /> blank casing and 0 020-inch-slot well screen with flush threads set from 40 to 45 feet bgs Six <br /> soil vapor extraction wells were installed in borings V-1 through V-6 using 2-inch-diameter, <br />' schedule 40 PVC blank casing and 0 020-inch-slot well screen with flush threads set from 13 <br /> to 30 feet bgs In all wells, a#3-sand filter pack was installed in the annulus from the bottom <br /> of each boring to at least 2 feet above the top of the well screen, followed by a well seal <br />' consisting of a 2-foot-thick hydrated bentonite layer overlain by neat cement to ground <br /> surface The bentonite layer was constructed above the water table with bentonite chips <br /> Each boring was then grouted using neat cement pumped through tremae up to grade Each <br />' well was secured by a locking expandable well cap and fitted with a traffic-rated well box set <br /> in concrete The groundwater in Well AS-1 was surged following the installation of the sand <br /> filter pack and prior to the installation of the bentonite seal Well completion details for the <br />' seven newly installed wells are presented in Table 2 and illustrated on the appropriate boring <br /> logs (Appendix B) <br /> File PAR-report doe SECOR International Incorporated <br /> I <br />
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