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3500 - Local Oversight Program
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PR0544612
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Last modified
7/1/2019 12:41:58 PM
Creation date
7/1/2019 11:24:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0544612
PE
3528
FACILITY_ID
FA0009287
FACILITY_NAME
NORTH STOCKTON AUTO SVC INC
STREET_NUMBER
8709
Direction
N
STREET_NAME
DAVIS
STREET_TYPE
RD
City
STOCKTON
Zip
95209
APN
07242018
CURRENT_STATUS
02
SITE_LOCATION
8709 N DAVIS RD
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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Ms. Lori Duncan <br /> Page 3 of 6 <br /> Based on historical groundwater monitoring data within close proximity to the site, current depth <br /> to water is expected to be approximately 28 to 30 feet below grade and is expected to flow in a <br /> northeasterly direction (San Joaquin County PHS/EHD Corresp, 9/6/00). Historical data from <br /> San Joaquin County Flood Control and Water Conservation District suggests that water levels are <br /> currently at or near a historical high. Historical low water levels are expected to have been <br /> between 45 and 50 feet bgs. <br /> 2.3 Investigations Undertaken <br /> In accordance with the approved workplan dated July 20, 2000, a total of five soil borings were <br /> advanced at the site to investigate the lateral and vertical extent of residual soil contamination, as <br /> well as the potential impact to groundwater. Boring SB 1 was located in the former UST <br /> excavation, and borings SB2 through SB5 were located around the perimeter of the UST <br /> excavation (Figure 2). The borings were advanced to depths ranging from 16.5 to 17 feet bgs <br /> where refusal was met due to a hard pan formation. <br /> 3.0 INVESTIGATIVE PROCEDURES <br /> On September 11, 2000, Fisch advanced the borings under the supervision of field geologist Sean <br /> Garvey, and project manager Greg Stahl, a California Registered Geologist. Ms. Lori Duncan of <br /> San Joaquin County Public Health Services, Environmental Health Division (PHS/EHD) <br /> conducted the site inspection and observed field activities. <br /> Fisch utilized a truck mounted Geoprobe 5400 direct push rig to advance the borings and collect <br /> soil samples. Soil samples were collected at 5-foot intervals using a 1 3/4 -inch diameter by 24-inch <br /> long core sampler. The sampler was lined with clear acetate sleeves, affording soil identification <br /> and subjective evaluation for contamination. A flame ionization detector (FID) was used to <br /> monitor the presence of volatile organic compounds in the soil. Soil samples from the borings <br /> were sealed, labeled, and immediately placed in an iced cooler for transport to Argon, a state- <br /> certified analytical laboratory. Soil samples were selected based on observations and field <br /> screening results. Due to the presence of a hardpan formation extending from approximately 15 <br /> bgs to unknown depths, groundwater samples were unable to be collected. <br /> Borings SB2, SB4 and SB5 were advanced to a depth of approximately 16.5 feet bgs. Borings <br /> SB 1 and S133 were advanced to a depth of approximately 17 feet bgs. Refusal was encountered in <br /> all borings due to a hardpan formation. <br /> The completed borings were backfilled to the ground surface with neat cement grout. No soil <br /> cuttings were generated. All down-hole drilling and sampling equipment was decontaminated by <br /> washing with a laboratory grade detergent and rinsing with water. Rinsate collected from <br /> decontamination procedures was disposed of via evaporation on the asphalt/concrete surface within <br /> the confines of the investigation area. <br /> Nsautolreports\summary_WP.doc <br />
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