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Draft Environmental Impact Report Page IV.E-4 <br /> I' p g <br /> Forward Inc. Landfill Expansion Project <br /> re-location, and associated site modifications necessitated by the expansion. The proposed <br /> expansion includes an increase in the number of allowable daily load deliveries to the landfill. <br /> The objective is to evaluated potential health risks that may occur as-a result of the proposed <br /> landfill expansion. The SCS (2008)risk assessment has been peer-reviewed by Stellar <br /> Environmental Solutions, Inc. prior to incorporation into this EIR. <br /> While there are no definitive nrtive standards for risk assessments specified by CEQA, all quantitative <br /> risk assessments are typically performed based in large part under standard guidelines set forth <br /> ' by the USEPA. Deviations from USEPA standards are outlined by state regulatory agencies <br /> such as the Cal/EPA. Evaluation of health risks in the SCS (2008) report is considered <br /> consistent with standard regulatory guidelines and risk assessment practice. The EPA has <br /> historically defined acceptable risk in a conservative manner for superfund sites as health risk <br /> from 30 year (residential) exposures that do not result an increase in cancer of reater than 1 in <br /> 1,000,000. The EPS target risk range is from 1 in 10,000 to 1 in 1,000,000 (1 x 10 to 1 x 10-6). <br /> Acceptable risks by the RWQCB (inherent for example.in their environmental screening levels) <br /> F generally fall within the range of between 1 in 100,000 to 1 in 1,000,000 (10-5 and 10-, <br /> respectively). <br /> The chronic non-carcinogenic risks in the Risk Assessment (SCS,2008)are presented as the ratio <br /> of the CDI to the RfD (CDL•RfD) resulting in a number called the Hazard Quotient(HQ). In <br /> addition,the acute risks for residential receptors were presented as the ratio of the receptor <br /> `i concentration or EPC to the Reference Exposure Levels (RELs) (EPC:REL). The sum of all of the <br /> CDI/RFD or EPC/REL ratios (i.e., HQs) of chemicals under consideration is called the Hazard <br /> Index.(HI). If the CDI or EPC is smaller than the RfD or REL, the HQ will be less than 1.0. If the <br /> CDI or EPC is larger than the RfD or REL,the HQ will be greater than 1.0. An HQ less than 1.0 <br /> 3 .F indicates that there is not likely to be any adverse health effects from the exposure. An HQ <br /> greater than 1.0 indicates that there is a potential health hazard for the exposed population. <br /> When a human population is exposed to several chemicals contaminants, such as with the <br /> Project, HQs for each of the contaminants are added together to produce the HI. As with the <br /> HQs, an HI less than 1.0 indicates that there is not likely to be any adverse health effects from <br /> the exposure while an HI greater than 1.0 indicates that there is a potential health hazard. The <br /> SJVAPCD CEQA guidelines have an HI threshold of significance of 1.0. This HI threshold of 1.0 <br /> was used as the CEQA significance level for evaluating the proposed Project scenarios. <br /> ra> <br /> To determine the lifetime cancer risk for a particular chemical contaminant, CSFs are multiplied <br /> }' by the CDI of the contaminant under consideration. The total lifetime cancer risk for a site is <br /> determined by summing all the individualized cancer risks for the various chemicals of <br /> concern. <br /> Chronic non-carcinogenic and carcinogenic risks are based on the average COPC emissions <br /> from the worst-case 30 years of emission levels. The 30-year average values were considered <br /> 1 appropriate for calculating long-term human health risks,which are generally based on 30 years <br /> of exposure rather than short-term exposure levels. <br /> The report focuses on quantifying potential health risks associated with off-site residents and <br /> off-site workers resulting from chemical emissions from the proposed landfill modifications. <br /> Specific off-site receptors evaluated include six residences, the Northern California Youth <br /> i Center, and the Northern California Women's Facility, all of which are located within a mile of <br /> the site. The HRA also evaluates potential exposures to on-site landfill workers through a <br /> screening with respect to applicable occupational hazards. Risks to the above receptors were <br /> "a estimated under both existing and proposed future expansion scenarios. The primary transport <br />