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SR2400480
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SR2400480
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Entry Properties
Last modified
7/17/2026 11:25:20 AM
Creation date
1/16/2025 4:08:50 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
SR2400480
PE
2900 - Site Mitigation Program
STREET_NUMBER
3457
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
17702078
CURRENT_STATUS
Active
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
3457 S AIRPORT WAY STOCKTON 95206
Tags
EHD - Public
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Vapor Intrusion Assessment Work Plan Project number:60653972 <br /> 4.2 Utility Clearance <br /> Prior to advancement of any tooling, an Underground Service Alert(USA)will be called into the 811 <br /> USA North system at least 48 hours in advance of any subsurface work. Once utility members have <br /> responded and/or marked their utilities at the Site,AECOM will have a private utility locator conduct <br /> utility clearance at each intrusive location. During this utility clearance,a 10-foot by 10-foot area <br /> surrounding each intrusive location will be cleared.In addition, each location will be hand-augered to a <br /> depth of 5 feet bgs. <br /> 4.3 Sub-Slab Soil Gas Sampling <br /> Sub-slab soil gas sampling will be used to assess whether vapors are present directly under selected <br /> buildings onsite, and to help assess the impact that sub-slab vapors may have on indoor air quality. Sub- <br /> slab samples will be collected in the air space immediately below the slab, and at depths of 5 and 15 feet <br /> below the slab,to characterize conditions beneath each building. Sub-slab samples will be co-located with <br /> IA samples. Sub-slab samples will be collected between 8 and 24 hours after the M samples are <br /> collected. Sample locations will be determined by accessibility to building interiors prior to sampling and <br /> the following rationale per DTSC VI Guidance(DTSC,2011 &2023). <br /> • Sub-slab soil gas samples will be located,when possible, at the center of the space away from doors <br /> and the foundation edge and within proximity of preferential pathways.Possible preferential <br /> pathways include bathrooms, areas of suspected chemical use, areas with underground utilities, floor <br /> drains, and/or plumbing features. Samples can also be placed in areas likely to have potential <br /> receptors. <br /> 4.3.1 Field Activities <br /> Permanent sub-slab soil gas probes with be installed at 12 locations, as shown on Figure 2 and described <br /> below.At each location soil gas probes will be installed as follows and as shown in Figure 3 <br /> • Access permitting,up to 12 permanent sub-slab soil gas probes will be installed, including two each <br /> in Buildings 6 and 9, one each in Buildings 2 and 3, and six in Building 4,near possible preferential <br /> pathways when accessible. <br /> • Sub-slab drilling locations will be marked and cleared of utilities (public and building specific).If <br /> the building has a tensioned slab the tension cables within the slab will be located prior to drilling <br /> either through visual observation or through remote sensing with ground penetrating radar. <br /> • The sub-slab probes placed immediately below the slab will be installed by removing any existing <br /> floor covering and drilling an approximate 1-inch-diameter hole through the building floor slab using <br /> an electric hand drill or concrete corer.The hole for the probe installation will be advanced 3 to 4 <br /> inches into the engineered fill beneath the building slab. The slab thickness and total depth of the <br /> probe drill hole will be recorded in the field notebook. <br /> • For the deeper probes,two screened intervals will be installed within one borehole with screens set <br /> immediately below the slab, and at 5 and 15 feet bgs. <br /> • Each sampling probe will be constructed using a 1/8-or 1/4-inch diameter tubing with a permeable <br /> probe tip at the end.After each probe is installed in the hole,the annulus around the probe tip will be <br /> filled with a sand pack centering the probe tip with at least 6 inches of sand above and below the <br /> level of the probe tip.After placing the sand pack,a dry granular bentonite transition seal will be <br /> added on top of each sand pack, followed by a hydrated bentonite annual seal(see Figure 3 showing <br /> typical sub-slab vapor probe design). The remainder of the hole will be filled with neat cement <br /> mixed with bentonite for a permanent probe. The concrete surface in the borehole will be cleaned <br /> Prepared for: California Regional Water Quality Control Board,Central Valley Region AECOM <br />
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