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2900 - Site Mitigation Program
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PR0542201
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COMPLIANCE INFO
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Last modified
6/1/2021 4:35:41 PM
Creation date
6/1/2021 4:13:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0542201
PE
2960
FACILITY_ID
FA0024238
FACILITY_NAME
JM EQUIPMENT COMPANY
STREET_NUMBER
1245
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16323034
CURRENT_STATUS
01
SITE_LOCATION
1245 W CHARTER WAY
P_LOCATION
01
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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ADVISORY- ACTIVE SOIL GAS INVESTIGATIONS <br />3.5 DECONTAMINATION <br />Decontaminate all reusable equipment to prevent cross contamination. Tubing is not <br />reusable and should not be decontaminated. Instead, use new or unused sampling <br />tubing for each probe location. <br />Decontamination may consist of steam cleaning or a three-stage decontamination <br />process consisting of a wash with a non-phosphate detergent, a rinse with tap water <br />and a final rinse with distilled water. Collect one equipment blank at the beginning of <br />sampling and at least one each day after decontamination. Equipment should be air- <br />dried before reuse. <br />The most common method of collecting an equipment blank is to pour distilled water <br />over recently decontaminated piece of equipment and collect the water in an <br />appropriate container for analysis of site constituents. Drill rods contacting contaminated <br />soil should be decontaminated before reuse and blank tested as appropriate. If soil gas <br />samplers arrive at the site after drill rig demobilization, equipment blanks should be <br />provided by the drilling contractor. As discussed in Section 3.2.2, an equipment blank is <br />recommended for probe tubing and probe tips. A syringe blank may be collected by <br />sampling ultra-pure air as it passes through the syringe, and a syringe blank is not an <br />acceptable substitute for the driller's equipment blank. The equipment blanks <br />demonstrate there is no residual contaminant carryover from other sites or the <br />manufacturing process. <br />3.6 SUB-SLAB INVESTIGATION METHODS <br />The procedures for collecting sub-slab soil gas samples directly under a building's <br />foundation are the same as for collecting subsurface soil gas samples. When collecting <br />sub-slab samples, if a building is determined to have a moisture barrier and/or a tension <br />slab, special care should be given when hand-drilling through the concrete slab. In <br />particular, for tension foundation slabs, the tension cables within the slab should be <br />located prior to drilling either through visual observation or through remote-sensing with <br />either a metal detector or ground penetrating radar. The cutting of a tension cable within <br />a slab during drilling could disrupt the integrity of the slab and potentially cause injury to <br />the field crew. <br />When evaluating sub-slab soil gas for a building, permanent sampling points should be <br />installed so repeated sampling can be conducted, as necessary, to evaluate seasonal <br />or temporal variations. <br />For sub-slab samples, after removal of the floor covering, a small-diameter hole should <br />be drilled through the concrete of the foundation slab. Typically, holes are 1.0 to 1.25 <br />inches in diameter. Either an electric hand drill or concrete corer is used to drill the <br />holes. All sub-slab utilities, such as water, sewer, and electrical, should be located and <br />clearly marked on the slab prior to drilling. Sub-slab holes should be advanced three to <br />four inches into the engineering fill below the slab. All drill cuttings should be removed <br />from the borehole. A typical sub-slab probe design is shown in Figure 2. The sampling <br />probe should be constructed with the following specifications: <br />July 2015 15
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