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Last modified
1/31/2020 6:00:03 PM
Creation date
1/31/2020 4:30:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0545272
PE
3528
FACILITY_ID
FA0006898
FACILITY_NAME
RAMOS OIL-FRENCH CAMP
STREET_NUMBER
10842
Direction
S
STREET_NAME
HARLAN
STREET_TYPE
RD
City
FRENCH CAMP
Zip
95231
APN
19333028
CURRENT_STATUS
02
SITE_LOCATION
10842 S HARLAN RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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Tvrnin 11I <br /> MB Environmental Geology 8613 Walnut Ridge Way <br /> Sacramento, California 95828 <br /> (916) 681-1168 <br /> i /lN� 11 <br /> January 11,2005 FEB 1 0 2005 <br /> 1, ENVIRONMENT HEALTH <br /> f PERMIT/SERVICES <br /> Mr.Kent Ramos <br /> Ramos Oil Company <br /> P.O. Box 401 <br /> West Sacramento, California 95691 <br /> Subject: Limited Phase Illnvestigation Results <br /> Beneto Oil Cardlock Fuel Facility <br /> 10855 South Harlan Road <br /> French Camp,California <br /> Dear Mr.Ramos, <br /> MB Environmental Geology (MBEG) was contracted by Ramos Oil Company (Ramos) to drill five <br /> Geoprobe soil borings at the Beneto Oil cardlock fuel facility located at 10855 South Harlan Road, <br /> French Camp, California. The borings were advanced in the vicinity of the diesel fuel dispensers, <br /> product piping, and 20,000-gallon diesel underground storage tank (UST). A site map illustrating site <br /> features and the soil sample locations is provided in Enclosure A. A drilling permit was required by <br /> the San Joaquin County Environmental Health Department; a copy of the drilling permit is included in <br /> Enclosure B. <br /> On December 20, 2004, under MBEG's supervision, Fisch Environmental drilled five soil borings <br /> (GP-1 through GP-5) at the subject property utilizing a hydraulic, direct-push (Geoprobe) drill rig. <br /> The borings were drilled to depths ranging from 8 to 32 feet beneath surface grade (bsg). Discrete soil <br /> samples were collected at 4 and 8 beneath surface grade (bsg) in the four borings (GP-1, GP-2, GP-4 <br /> and GP-5) adjacent to the dispenser islands and at 16 and 20 feet bsg from the boring (GP-3) adjacent <br /> to the UST. The soil samples were collected from each location using 1-inch diameter by 2-foot long <br /> acetate sample liner using hydraulic direct-push technology. Immediately following collection, the <br /> sample tube was sealed on each end with a TeflonT' membrane and a plastic cap. The sample was <br /> stored on ice pending transportation to the laboratory. Each of the soil samples was screened with a <br /> photoionization detector (PID). The PID readings were zero for each sample screened. The lithology <br /> encountered in the soil borings consists primarily of At and clay that contains thin, discontinuous beds <br /> of fine sand/silty sand. Copies of the soil boring logs are included in Enclosure C. Groundwater <br /> samples were collected from borings GP-1 through GP-3 using a Hydropunch sampling device. <br /> The soil and groundwater samples were submitted to Kiff Analytical laboratory in Davis, California for <br /> analysis of total petroleum hydrocarbons(TPH)as diesel by EPA Method 8015 Modified. Copies of the <br /> laboratory analytical report with chain-of-custody documentation for the soil and groundwater samples <br /> collected are included in Enclosures D and E, respectively. Laboratory analytical results reported low <br /> levels of TPH as diesel in each of the soil and groundwater samples for analysis. Concentrations of TPH <br /> as diesel were reported in soil at concentrations ranging from 3 to 11 milligrams per kilogram (mg/kg) <br /> and concentrations in groundwater at concentrations ranging from 89 to 240 micrograms per liter. <br /> Helping Businesses Solve Environmental Problems <br />
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