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2900 - Site Mitigation Program
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PR0540108
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Last modified
7/24/2019 9:02:34 AM
Creation date
7/24/2019 9:01:57 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0540108
PE
2960
FACILITY_ID
FA0022809
FACILITY_NAME
CASA DE OASIS - MULTI-FAMILY HOUSING FACILITY
STREET_NUMBER
1700
Direction
S
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
16703326
CURRENT_STATUS
01
SITE_LOCATION
1700 S EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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07 May 2015 • • <br /> AGE Project No. 15-3325 <br /> Page 3 of 4 <br /> SOIL-VAPOR SAMPLING <br /> Proposed soil borings may be advanced using truck-mounted or limited-access <br /> hydraulic direct-push drill rigs equipped with 1.25-inch probing rods. The drill rigs <br /> advance soil probe borings using a hydraulic hammer to drive soil and groundwater <br /> sampling tools to specified depths. <br /> Alternatively, soil borings may be advanced using a small diameter steel probe sampler <br /> with retractable screened vapor points driven into the subsurface with a mechanical <br /> hand-held hammer (rotohammer). <br /> Sampling points will be advanced to a depth of 5 or 10 feet bsg by driving a 1.5 inch tip <br /> on 1.25 inch rods to depth. The rods will then be removed and a temporary vapor probe <br /> will be attached to '/4 inch disposable polyethylene tubing. Sand will be poured to a <br /> depth of one-foot above the screen interval. Three to six-inches of dry bentonite <br /> followed by one-foot of hydrated bentonite will be placed above the sand. The <br /> remainder of the borehole will be filled with either hydrated bentonite or grout. Hydrated <br /> bentonite will be placed around the tubing at the surface to further prevent ambient air <br /> intrusion. <br /> An onsite mobile lab will be used for sample collection and analysis the next day. The <br /> mobile lab will determine the purge volume and use a tracer gas of either IPA or 1,1- <br /> difluouroethane (1,1-DFE) during field sampling activities. All samples will be run onsite <br /> following sample collection, using EPA Method 82608. <br /> Following sample collection the total VOC concentration in the sample probes will be <br /> measured using a hand-held photo-ionization detector (PID; Rae Mini-rae). <br /> INDOOR AND AMBIENT AIR MONITORING AND SAMPLING <br /> AGE proposes to collect one indoor air sample in the community center building. Indoor <br /> air samples will be collected in six-liter Summa canisters using passive integrated <br /> sampling procedures. Each canister's initial vacuum will be measured and recorded to <br /> ensure the initial vacuum is greater than 25 inches of mercury (in hg). The sampling <br /> inlet on the canisters will be connected to a mass flow controller containing a particulate <br /> filter and calibrated to 3.8 milliliters/minute (ml/min). Air samples will be collected over a <br /> period of approximately 24 hours based on the calibrated flow of 3.8 ml/min. <br /> Indoor air samples will be collected in the southwest corner of the community center <br /> room and will be placed approximately three to five feet above the ground surface in the <br /> breathing zone. The Summa canister will then be opened to begin air sample collection. <br /> Following 24-hours of sample time, the containers will be retrieved, closed, and sealed. <br /> Advanced GeoEnvironmental,Inc. <br />
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