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2900 - Site Mitigation Program
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PR0548037
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Entry Properties
Last modified
7/17/2026 11:48:18 AM
Creation date
7/23/2025 2:39:16 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0548037
PE
2950 - ENVIRON ASSESS
FACILITY_ID
FA0027411
FACILITY_NAME
CITY OF LODI PARKS AND RECREATION DEPARTMENT
STREET_NUMBER
125
Direction
N
STREET_NAME
STOCKTON
STREET_TYPE
ST
City
LODI
Zip
95240
APN
043084130
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
125 N STOCKTON ST LODI 95240
Tags
EHD - Public
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Sampling and Analysis Plan for Phase II Environmental Site Assessment <br /> 125 North Stockton Street, Lodi,CA 95240 <br /> Collected samples will be placed into laboratory-supplied containers for shipment to the <br /> analytical laboratory. <br /> Following completion of sampling activities, the boreholes will be backfilled with neat cement <br /> grout or hydrated bentonite in accordance with permit requirements and patched with like <br /> materials to match existing grade. <br /> 3.2.2 Soil Vapor Sampling <br /> Four temporary soil borings will be extended to approximately 15.5 feet bgs using direct-push <br /> equipment and installed with dual-nested temporary soil vapor probes. Each soil vapor probe will <br /> consist of a stainless-steel inlet fitting connected to Nylaflow® tubing. The inlet fitting will be <br /> installed at approximately 5 and 15 feet bgs within one foot of bedding sand. The overlying <br /> annular space will be filled with approximately six inches of dry, granular bentonite, and the <br /> remaining annular space will be filled with granular bentonite and hydrated in six-inch lifts. <br /> Soil vapor probes will be allowed to equilibrate for a minimum of 48 hours before sampling, in <br /> accordance with DTSC guidance. Samples will be collected into laboratory-supplied Summa <br /> canisters with dedicated flow controllers set at approximately 175 milliliters per minute. Prior to <br /> sampling, the sample collection "train" will be tested for tightness by isolating the canister and <br /> flow controller fittings and applying a vacuum of 7.5 inches mercury using a three-way valve and <br /> syringe.The shut-in test will be considered complete if the apparatus is able to hold vacuum for a <br /> period of at least one minute. If leaks are observed, the fittings will be tightened and re-tested. <br /> Prior to sampling, the soil vapor probe will be purged of three volumes of air, corresponding to the <br /> calculated volume of air within the tubing and the pore space of the bedding sand. During <br /> sampling, the sampling apparatus will be placed beneath a sampling shroud, and helium gas <br /> applied as a leak check compound at a concentration of approximately 30 percent by volume, <br /> as determined using a helium detection meter.Sampling will continue until the vacuum gauge on <br /> the Summa canister registers approximately 5 inches mercury. Summa canisters will be labeled <br /> and transported to the analytical laboratory for analysis. <br /> Following completion of sampling activities, the temporary probes will be removed, and the <br /> surface patched with like materials to match existing grade where sampling is conducted in areas <br /> of existing pavement. <br /> 3.2.3 Sample Handling and Analysis <br /> Soil and soil vapor samples will be transported to Pace National laboratory under chain-of-custody <br /> protocol for chemical analysis. Consistent with the QAPP, sample designations will incorporate <br /> three components as summarized below: <br /> Location Code Sample Type Depth Interval Example <br /> 131, 132, 133, 134 Soil 0.5-1 ft, 3 ft, 5 ft B 1-S-1, B 1-S-3 <br /> 131, B4, B6, B10 Soil vapor 5 ft, 15 ft B1-SV-5, B1-SV-15 <br /> Stantec 11 <br />
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