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2900 - Site Mitigation Program
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PR0542458
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COMPLIANCE INFO
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Last modified
8/8/2024 8:39:15 AM
Creation date
6/11/2021 9:24:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0542458
PE
2960
FACILITY_ID
FA0024399
FACILITY_NAME
PARKWOODS CLEANERS
STREET_NUMBER
1744
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
07728032
CURRENT_STATUS
01
SITE_LOCATION
1744 W HAMMER LN
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\gmartinez
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EHD - Public
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GSI Job No.: 14� G S 1T <br /> Issued: 15 November 2017 <br /> ENVIRONMENTAL <br /> 5.3 Soil Sample Collection Procedures <br /> Soil borings will be advanced using direct-push drilling techniques with dual-cased drilling rods to <br /> collect soil samples for VOC analysis and lithologic description, maintain a cased boring between <br /> sample retrieval runs to minimize the potential for cross-contamination between sample intervals, <br /> and to facilitate the installation of temporary soil gas probes. <br /> Soil sampling collection procedures are further described in the following subsections. <br /> 5.3.1 Soil Sample Collection <br /> Recovered soil will be screened for the presence of VOCs using a photoionization detector (PID) <br /> as recovered soil is removed from the drive samplers and initially observed, and also in head <br /> space samples from intermittent depths. Soil samples will be collected from select depths using <br /> US EPA Method 5035 field methods for the preservation of VOCs. GSI will collect soil samples <br /> from each boring based on lithology and results of PID screening. Preliminary target intervals for <br /> soil sampling are from depths of 2 to 2.5 feet bgs, 4.5 to 5 feet bgs, 9.5 to 10 feet bgs, and 14.5 <br /> to 15 feet bgs. <br /> GSI will describe soil boring lithology in accordance with ASTM Method D2488 visual-manual <br /> methods/the Unified Soil Classification System (USCS). Observations will be recorded on boring <br /> log sheets, along with soil sample collection intervals and results of soil core screening using a <br /> PID. <br /> 5.3.2 Sampling Packaging, Shipment, and Chain-of-Custody <br /> Each soil sample will be identified with a sample-specific identification code linking the sample to <br /> descriptive information recorded in field documents (including boring identification and sample <br /> depth). A separate label will be affixed to each sample container with a self-adhesive backing <br /> and a record of samples submitted to the laboratory will be entered onto a chain of custody form. <br /> The samples will be placed in an ice-filled chest and transported to the analytical laboratory under <br /> chain-of-custody procedures. <br /> 5.3.3 Equipment Decontamination <br /> To reduce the potential for cross-contamination, re-usable sampling equipment will be <br /> decontaminated using laboratory-grade detergent and potable water, and rinsed twice with <br /> potable water, or by using a high pressure steam cleaner. <br /> 5.3.4 Equipment Calibration and Maintenance <br /> The PID used during the investigation will be maintained and calibrated according to manufacturer <br /> specifications. GSI will calibrate the PID once a day, at a minimum, before starting work activities. <br /> 5.4 Soil Sample Analysis <br /> Select soil samples will be analyzed for VOCs by US EPA Method 8260B by a California <br /> Department of Public Health Environmental Laboratory Accreditation Program (ELAP) certified <br /> laboratory. <br /> 5.5 Soil Gas Sampling and Analysis <br /> The soil gas investigation will be conducted in general accordance with the July 2015 California <br /> Environmental Protection Agency's Advisory — Active Soil Gas Investigations (Advisory). <br /> Site Investigation Work Plan <br /> Park Woods Cleaners <br />
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