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WILLOW GLEN
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13751
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2900 - Site Mitigation Program
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PR0009025
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Last modified
5/19/2021 3:14:56 PM
Creation date
5/19/2021 12:31:59 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0009025
PE
2960
FACILITY_ID
FA0004055
FACILITY_NAME
LATHROP GAS DEHYDRATOR
STREET_NUMBER
13751
Direction
S
STREET_NAME
WILLOW GLEN
STREET_TYPE
RD
City
STOCKTON
Zip
95206
APN
19105010
CURRENT_STATUS
01
SITE_LOCATION
13751 S WILLOW GLEN RD
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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results of field screening suggest that soil and/or groundwater is impacted in the primary boreholes, three <br /> additional borings (secondary borings) will be drilled adjacent to the south, west, and north property lines <br /> and samples of the soils and groundwater will be collected (Figure 2). <br /> The boreholes will be drilled using a drill rig equipped with 8 or 10-inch O.D. hollow-stem, continuous-flight <br /> augers. The exact number and location of the boreholes may change based on conditions encountered <br /> during the field activities. The exploratory borings will be drilled to first encountered groundwater to facilitate <br /> soil and groundwater sample collection. Samples of the subsurface soils will be collected at intervals no <br /> greater than 5 feet using a 2-inch or 2 ,h-inch I.D. split spoon sampler, a standard penetration sampler, or <br /> a continuous coring device. All drill bits, drill rods, augers, etc. will be steam-cleaned prior to each use. <br /> The following procedures will be employed when collecting and handling soil samples: <br /> 1. Prior to sampling, the split spoon sampler (or equivalent) and sample liners will be thoroughly <br /> washed with a solution of Alconox or non-phosphate TSP and rinsed with potable water. <br /> 2. The samples will be retained in the sample liners with the ends covered with aluminum foil or <br /> Teflon sheets and plastic end caps. <br /> 3. Each sample will be labeled using waterproof ink with the job name, job number, boring number, <br /> sample depth, date collected, and the initials of the person who collected the sample. <br /> 4. A description of the soil sample will be entered on a boring log form by the field geologist. This <br /> description will include soil classification (ASTM D-2487-83), color, moisture content and <br /> consistency (in relative terms), and estimated degree of hydrocarbon content as measured using <br /> a photoionization detection (PID) meter. <br /> 5. Immediately after sample collection and labeling, the samples will be sealed in a plastic bag and <br /> placed in a sturdy ice chest. The temperature in the ice chest will be maintained at or below 4°C. <br /> 6. When the ice chest is full (or contains all the samples which will be stored in it), a completed <br /> chain of custody form will be inserted and the chest will be closed and sealed. <br /> Groundwater grab samples will be collected from each borehole in the upper portion of the first water- <br /> bearing zone. Two-inch diameter PVC well screen and casing will be inserted into each borehole to allow <br /> groundwater sampling and water level measurements. The well screen will be 5 to 10 feet in length and will <br /> extend across the water table surface. A filter sock will be placed over the well screen to control turbidity <br /> in the groundwater samples. The groundwater samples will be collected by lowering a bailer through the <br /> casing immediately after the borehole is drilled and the augers are removed from the hole. The bailer <br /> contents will be carefully transferred into the appropriate sample containers. The groundwater samples will <br /> be submitted for chemical analyses to a State of California-certified laboratory (Chromalab, San Ramon). <br /> The well screen and casing will remain in each borehole until the water level in each borehole has stabilized <br /> (but not for a period longer than 24 hours per San Joaquin County requirements). Once the water <br /> cca/9-30-92/8913a/JAWP13 8 <br />
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