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EHD Program Facility Records by Street Name
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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 /> ASSomns,iNc. <br /> PAGE 7 <br /> packs to the laboratory <br /> 2.7 DUPLICATE AND EQUIPMENT BLANK COLLECTION <br /> Duplicate soil gas samples will be collected at each site as required in the site-specific quality <br /> assurance project plan and field sampling plan. Generally, one duplicate sample will be collected <br /> for every ten samples collected. Each duplicate is collected in conjunction with a corresponding <br /> environmental sample. <br /> To collect duplicate samples in Tedlar® bags, a Y-branched sampling hose will be connected to <br /> the vacuum chamber or pump. Two Tedlar® bags are then attached, one to each end of the <br /> Y-branched hose. Syringe duplicate sampling is performed by collecting and analyzing a <br /> subsequent sample. To collect duplicate samples in canisters, a Swagelok "T"will be connected <br /> to two canisters. Purging and sample collection will proceed as described above. After collection, <br /> one sample will be labeled as the environmental sample and one as the duplicate. <br /> Equipment blanks also will be collected at each site as required in the site-specific quality <br /> assurance project plan and field sampling plan. Generally, one blank will be collected for every <br /> ten samples collected. Blanks will be collected by running ambient air through the sampling <br /> system immediately after it has been decontaminated,and by collecting the ambient air in a Tedlar® <br /> bag, Summa canister, or sorbent tube using the same procedures used to collect environmental <br /> samples. Blank sample collection is conducted upwind of any observed interference, and the <br /> location of the sampling must be recorded in a field logbook. Equipment blanks are collected to <br /> ensure that field equipment decontamination procedures are adequate. <br /> 2.8 LEAK CHECK PROCEDURES <br /> Leakage during soil gas sampling may dilute samples with ambient air and produce results that <br /> underestimate the actual site concentrations, or may contaminate the sample with external <br /> contaminants. Leak tests should be conducted to determine whether leakage is occurring. Leak <br /> detection is performed using the following procedures: <br /> 1. Leak tests should be conducted at every soil gas probe. <br /> 2. Tracer compounds such as isopropanol, butane, helium, or 1,1-difluoroethane may be <br /> used as leak check compounds. These compounds may be contained in common <br /> products such as Dust-Off and rubbing alcohol. Be sure the tracer compound used does <br /> not contain chemicals or impurities that may be present as a site contaminant. <br />
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