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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/14/2019 3:46:08 PM
Creation date
2/14/2019 9:40:06 AM
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0517323
PE
2960
FACILITY_ID
FA0013339
FACILITY_NAME
MT HOUSE SITES 1-6
STREET_NUMBER
0
STREET_NAME
BYRON
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
BYRON RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Human Health Screening Evaluation <br /> Mountain House Development Site#6 January 18,2011 <br /> incremental lifetime cancer risk; EPA, 1989). SAIC summed the potential cancer health risks for <br /> each individual chemical in an exposure pathway to estimate an overall cancer risk for each <br /> exposure pathway; and then summed the cancer risks across all evaluated exposure pathways to <br /> estimate incremental lifetime cancer risk for the individual. <br /> SAIC estimated potential non-cancer health hazards for on-site residential child receptors by <br /> comparing estimated on-site doses to an acceptable reference dose exposure. SAIC evaluated the <br /> calculated ratio of the estimated dose to the reference dose (the hazard quotient) for potential <br /> exposure to each COPC, then summed the potential health hazards for each chemical in an <br /> exposure pathway to estimate the total health hazard for each exposure pathway. SAIC <br /> subsequently summed the health hazards across all evaluated exposure pathways to estimate the <br /> total hazard index for the receptor. <br /> In accordance with the National Contingency Plan, an incremental lifetime cancer risk of 1E-06 <br /> was used as a point of departure, and an excess cancer risk equal to or below this threshold is <br /> considered to be insignificant. The agency reviewing this HHSE will make risk management <br /> decisions on a site-specific basis if the excess cancer risk is within the acceptable range between <br /> 1E-04 and 1E-06. A hazard index of 1 or less for non-cancer hazards is considered to be an <br /> acceptable health hazard level. If the regulatory criteria are exceeded based on the screening <br /> evaluation, this evaluation identifies the chemical and the exposure pathways contributing to the <br /> elevated risks or hazards, which can be more precisely assessed in a site-specific refined health <br /> risk assessment, if warranted. <br /> 5.1 RESIDENTIAL CANCER RISKS <br /> SAIC calculated the oral and dermal cancer risks and inhalation cancer risks to potential on-site <br /> residential receptors for exposure to on-site soils using the following equations: <br /> Oral and Dermal Cancer Risks for Direct Contact with Soil (PEA Guidance Manual, Figure 2.3): <br /> Risksoii=(SFo x Cs x [1.57E-061) + (SFo x Cs x [1.87E-05] x ABS) <br /> Where: <br /> Risksoil=oral and dermal cancer risks from direct soil exposure <br /> SFo= oral cancer slope factor, (mg/kg-day)-' <br /> Cs= concentration in soil, mg/kg <br /> ABS = dermal absorption fraction, dimensionless <br /> The oral and dermal cancer risk calculations for potential exposures to on-site soils are provided <br /> in Table 8. Potential cancer risks were estimated for carcinogenic COPCs and then summed <br /> among chemicals for oral and dermal exposures. <br /> Inhalation Cancer Risks for Air(PEA Guidance Manual, Figure 2.4): <br /> Riskair= SM x Ca x 0.149 <br /> Where: <br /> Risk,,,,—inhalation cancer risk from indirect soil exposure <br /> SFi= inhalation cancer slope factor, (mg/kg-day)-' <br /> from sclence to SOIUNOF18 <br />
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