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ARCHIVED REPORTS XR0000215
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3500 - Local Oversight Program
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PR0543430
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ARCHIVED REPORTS XR0000215
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Last modified
2/5/2019 11:04:09 AM
Creation date
2/5/2019 10:44:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000215
RECORD_ID
PR0543430
PE
3528
FACILITY_ID
FA0009377
FACILITY_NAME
CAL TRANS MAINT SHOP 10
STREET_NUMBER
1603
Direction
S
STREET_NAME
B
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
16918002
CURRENT_STATUS
02
SITE_LOCATION
1603 S B ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
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EHD - Public
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I <br /> 1 SECTIOMT E Technical Approach <br /> • what the potential concentrations in groundwater at different distances may be, a Tier 3 RBCA is <br /> proposed for the site In conducting a Tier 3 assessment, an alternative model is required and the Jury <br /> model is being proposed <br /> The Jury Behavior Assessment Mo <br /> del (Jury et al, 19$3) can be used to calculate chemical mass <br /> loading from sort to groundwater and volatile emission rates from sort The Jury model is a semi- <br /> analytical model that directly estimates contaminant leachate to groundwater and volatilization <br /> emissions to the atmosphere The model accurately conserves mass The results of the Jury model can <br /> be used as a check on the ASTM RBCA results and a potential range of model estimates can be used <br /> in the risk assessment Data requirements listing physical and chemical parameters for the Jury Model <br /> are listed in Tables 3-1 and 3-2 <br /> The loading rate (calculated in the Jury model) of contaminants from soil leaching to groundwater is <br /> used as input to the saturated zone model, AT123D (Yeh, 1981) AT123D is a semi-analytical model <br /> that uses site-specific data related to the contaminant source, saturated zone, and the distance to the <br /> receptor well to estimate concentrations in the well Data requirements for AT123D are listed in Table <br /> 3-3 The volatile emission rate from the Jury model is used as input to an air dispersion model, the Box <br /> Model Fate and transport modeling will be conducted for a 70-year time period <br /> Site-specific data will be used whenever available as input data for both the ASTM RBCA and <br /> Jury/AT123D modeling For input parameters that do not have site-specific data, either data from the <br /> literature or default values will be used that are protective of human health and the environment All <br /> input values will be referenced as to their source <br /> Results from ASTM RBCA and Jury will be compared with current Federal and State Maximum <br /> Contaminant Levels(MCLS)for drinking water <br /> 3.9.5 Estimate Chemical Intake for All Receptors <br /> Chemicals are typically taken into the bodies of human populations by inhalation, ingestion, and dermal <br /> contact The intake of chemicals will be estimated using site-specific data, appropriate assumptions, <br /> and guidance from U S EPA's Exposure Factors Handbook The estimated intake will be based on the <br /> receptor population's activity patterns,local meteorology, and land use issues <br /> Proposed intake assumptions are listed on Tables 34 through 3-7 <br /> ® rt,se7Yer A%STOCKTOtAtEPOftToocy7.ALK14M,ers009Nn%SNu► 3-6 <br />
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