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2900 - Site Mitigation Program
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PR0516247
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Entry Properties
Last modified
6/23/2026 3:45:06 PM
Creation date
7/14/2021 9:12:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0516247
PE
2960 - RWQCB LEAD AGENCY CLEAN UP SITE
FACILITY_ID
FA0012531
FACILITY_NAME
CITY OF LODI-CENTRAL PLUME
STREET_NUMBER
221
Direction
W
STREET_NAME
PINE
STREET_TYPE
ST
City
LODI
Zip
95241
APN
04303111
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
221 W PINE ST LODI 95241
Tags
EHD - Public
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Soil Vapor Assessment Work Plan Page 5 <br /> CPSA,Lodi,California <br /> January 11,2023 <br /> METHODOLOGY <br /> Prior to installation of the TSV probes, CHT proposes to install soil borings at SV 1 and SV2 to a <br /> depth of 40 feet below ground surface(ft-bgs)using continuous soil coring. The soil cores,which <br /> will be collected in acetate liners, will be used to log the soil, and determine the screen intervals <br /> for all of the targeted temporary soil vapor probe depths. TSV probes will then be installed near <br /> SVI and SV2 in accordance with the DTSC's Advisory- Active Soil Gas Investigations <br /> (DTSC, 2012). The TSV probes will be installed using a dual-purpose limited access rig. At each <br /> soil vapor sampling location,the drill rig will advance the rods to a total depth of 40 ft-bgs in one <br /> boring where the 40 foot TSV probe will be installed, and then drill separate borings for installing <br /> the TSV probes at depths of 5, 10, 20, and 30 ft-bgs. The exact depth of the TSV probes will be <br /> determined from the soil core samples. <br /> Each TSV probe will be constructed with a 1-foot long filter pack in the bottom of the borehole <br /> consisting of#2/12 Cemex sack sand. A 0.250-inch outside diameter(0.187-inch inside diameter) <br /> polyethylene tube with a HDPE filter at the bottom of the tube will be placed in the center of the <br /> borehole during placement of the sand so that the HDPE filter is located in the center of the sand <br /> interval. The annular space above the sand will be temporarily sealed using hydrated bentonite <br /> slurry that will be pumped down the hole using tremie pipes to a height of 0.5 feet above the top <br /> of the sand. This would ensure that representative soil vapor samples are collected for each <br /> specified depth. <br /> SAMPLING <br /> The soil vapor samples will be collected in accordance with the sampling protocols established in <br /> the Advisory (DTSC, 2012). Soil vapor samples will be collected in individual certified 1-liter <br /> SUMMA® canister where the SUMMA® canister will supply the vacuum to draw soil vapor into <br /> the canister for analysis. The TSV probes will be purged and sampled in accordance with <br /> Section 4 (Soil Gas Sample Collection) and leak detection will be performed in accordance with <br /> Section 4.2.2.1 (Leak Check Compounds [Liquid]) of the Advisory. CHT proposes to use helium <br /> as the leak detection compound. <br /> Following soil vapor sample collection, a PID will be connected to the polyethylene soil vapor <br /> probe tubing to obtain a preliminary field value for the sample collection location. Measurements <br /> of vacuums, purging and equilibration time intervals, and PID readings will be recorded on Soil <br /> Vapor Sampling Data Sheets. The SUMMA® canister soil vapor samples will be delivered under <br /> chain-of-custody protocols to a California-certified laboratory for testing by EPA method TO-15 <br /> analysis for chlorinated VOCs. Additionally, the leak detection compound (helium) will be <br /> analyzed using Modified ASTM Method D-1946. <br /> Upon completion of sampling activities, the TSV probes will be abandoned by removing <br /> temporary well points and sealing the borehole with a neat cement grout or by using the appropriate <br /> method approved by SJDEH. <br /> 649 DISTEL DRIVE,LOS ALTOS,CA 94022 TEL:415-424-3009 <br />
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