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2900 - Site Mitigation Program
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PR0516614
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Last modified
5/31/2019 3:43:11 PM
Creation date
5/31/2019 3:23:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0516614
PE
2960
FACILITY_ID
FA0012708
FACILITY_NAME
NEWARK SIERRA PAPERBOARD/ RECYCLING
STREET_NUMBER
800
Direction
W
STREET_NAME
CHURCH
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14523004
CURRENT_STATUS
02
SITE_LOCATION
800 W CHURCH ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Geosyntec <br /> consultants <br /> Soil behavior type (SBT) will be interpreted using relationships between these <br /> parameters. The SBT log from each location will be evaluated and used to select up to <br /> two groundwater sampling depth interval(s). <br /> 2.2.3 Membrane Interface Probe(MIP) <br /> In order to further delineate the distribution of toluene previously detected in deeper soil <br /> near the northwest corner of the former Site building, a grid of six MIP borings will be <br /> advanced. <br /> The MIP is a direct push tool .used in situ to provide real-time, discrete depth <br /> information on the subsurface distribution of volatile organic compounds (VOCs), <br /> including toluene. The.MIP sensor consists of a semi-permeable membrane located a <br /> few inches above a direct push drill rod. An inert carrier gas, typically nitrogen, <br /> circulates through tubing within the drill rod and sweeps behind the membrane in the <br /> sensor at a flow rate of approximately 20 to 60 milliliters per minute (mL/min). VOCs <br /> diffuse across the membrane due to a concentration gradient between the subsurface and <br /> the clean carrier gas. A heating block located slightly below the membrane helps <br /> accelerate diffusion.- As the MIP sensor is advanced downward, volatile constituents <br /> are swept upwards within the drill rods via the carrier gas tubing to detectors at the <br /> surface. Detector responses are correlated to probe depth, yielding a log of detector <br /> response and temperature (used to identify the approximate elevation of groundwater) <br /> versus depth (approximately 0.1 to 0.2 feet vertical resolution).- Three detectors may be <br /> used in conjunction with a MJP: a photoionization detector (PID), an electron capture <br /> detector (ECD), and,a flame ionization detector (FID). In general, a PID responds to <br /> most VOCs and is particularly sensitive to aromatic hydrocarbons like benzene and <br /> toluene; an ECD responds to chlorinated VOCs such as TCE; and a FID responds to a j <br /> broader range of hydrocarbons. The MIP software can process up to four detector <br /> signals at.one time and provides plots of the detector readings versus depth. <br /> Vironex of Concord, California will provide the MIP module, which will be used in <br /> conjunction with the CPT. The MIP module fits behind the standard cone and is pushed <br /> into the ground where it acts as an interface between the contaminants in the subsurface <br /> and gas phase detectors at the surface. As shown on Figure 4, the six MIP borings will <br /> be advanced in a grid arrangement.. Each MIP boring will be advanced to a target total <br /> depth of approximately 40 ft bgs with the final depth of each boring determined in the <br /> field based on the observed MIP response. <br /> Final Work Plan>doc 7 27 June 2012 <br /> i <br />
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