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STOCKTON
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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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TO E RO E K SOP No.021,REV.1 <br /> „ SOIL GAS SAMPLING METHODS <br /> ASSOCIATES,INC. <br /> PAGE 8 <br /> 3. Place tracer compounds around the soil gas well at the ground surface and at all <br /> connections in the aboveground sampling system train. Tracer compound is emplaced <br /> by wetting or spraying a paper towel or rag and wrapping around the area of the <br /> connation where leaks could occur. <br /> 4. Collect samples as describe in previous sections and use analytical results to determine <br /> if the tracer compound has leaked into the sample. <br /> 2.9 DECONTAMINATION <br /> Sampling probes should be decontaminated before the first sample is collected and between <br /> sampling points. Probes that are grossly contaminated should be decontaminated using a <br /> high-pressure steam cleaner. Probes that are not grossly contaminated can be decontaminated by <br /> brushing off loose soil particles, then heating the probes until they are warm to the touch to drive <br /> off any volatile contaminants. Heating times of 7 to 10 minutes are generally sufficient for this <br /> purpose. This brushing and heating method greatly reduces the generation of decontamination <br /> fluids. <br /> Syringes must be decontaminated between each use. Sampling syringes must be disassembled and <br /> baked at 240°C for a minimum of 15 minutes or at 120°C for a minimum of 30 minutes, or must <br /> be replaced. All canisters must be properly decontaminated by the laboratory as specified by <br /> appropriate EPA methods. <br /> If Y-branched tubing or any other sampling equipment is to be reused, it must also be <br /> decontaminated between sampling locations. <br /> 2.10 SAMPLE TRANSFER <br /> After collection, each sample container will be transported to the designated laboratory for <br /> analysis. In many cases, samples will be analyzed on site in a mobile laboratory. <br /> 2.11 ADVANTAGES AND DISADVANTAGES OF EACH SAMPLING METHOD <br /> Tedlar®bags are relatively inexpensive to use but can only be used once and then must be disposed <br /> of. If the soil formation being sampled has a low porosity and permeability, such as clay or silty <br /> clay, it may not be possible to inflate the Tedlar®bag with soil gas. Some regulatory agencies do <br /> not recommend use of Tedlar® bags to collect soil gas for VOCs analysis. Due to short holding <br /> times, Tedlar®bags should typically only be used for on-site or near-site analysis. <br />
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