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9 <br /> <br />CO, PM10, and PM2.5 emissions, which are collectively referred to as criteria air pollutants.11 Because the <br />LST method can only be applied to criteria air pollutants, this method cannot be used to determine <br />whether emissions from DPM, a known human carcinogen, will result in a significant health risk impact <br />to nearby sensitive receptors. As a result, health impacts from exposure to toxic air contaminants <br />(TACs), such as diesel particulate matter (DPM), were not analyzed, thus leaving a gap within the DEIR’s <br />analysis. <br />Second, the omission of a quantified HRA is inconsistent with the most recent guidance published by the <br />Office of Environmental Health Hazard Assessment (OEHHA), the organization responsible for providing <br />guidance on conducting HRAs in California. In February of 2015, OEHHA released its most recent Risk <br />Assessment Guidelines: Guidance Manual for Preparation of Health Risk Assessments.12 This guidance <br />document describes the types of projects that warrant the preparation of an HRA. Construction of the <br />Project will produce emissions of DPM, a human carcinogen, through the exhaust stacks of construction <br />equipment over a construction period of approximately 26 months (Appendix B, pp. 247). The OEHHA <br />document recommends that all short-term projects lasting at least two months be evaluated for cancer <br />risks to nearby sensitive receptors.13 Therefore, per OEHHA guidelines, we recommend that health risk <br />impacts from Project construction be evaluated by the DEIR. Furthermore, once construction of the <br />Project is complete, the Project will operate for a long period of time. As previously stated, Project <br />operation will generate approximately 11,546 daily vehicle trips, which will generate additional exhaust <br />emissions and continue to expose nearby sensitive receptors to DPM emissions (p. 5.14-11, Table 5.14- <br />5). The OEHHA document recommends that exposure from projects lasting more than 6 months be <br />evaluated for the duration of the project, and recommends that an exposure duration of 30 years be <br />used to estimate individual cancer risk for the maximally exposed individual resident (MEIR).14 Even <br />though we were not provided with the expected lifetime of the Project, we can reasonably assume that <br />the Project will operate for at least 30 years, if not more. Therefore, we recommend that health risks <br />from Project operation also be evaluated, as a 30-year exposure duration vastly exceeds the 2-month <br />and 6-month requirements set forth by OEHHA. This guidance reflects the most recent health risk policy, <br />and as such, we recommend that an updated assessment of health risks to nearby sensitive receptors <br />from Project construction and operation be included in a revised CEQA evaluation for the Project. <br />Third, by claiming a less than significant impact without conducting a quantified HRA to nearby, existing <br />sensitive receptors as a result of Project construction, the DEIR fails to compare the excess health risk to <br /> <br />11 “Final Localized Significance Threshold Methodology.” SCAQMD, Revised July 2008, available at: <br />http://www.aqmd.gov/docs/default-source/ceqa/handbook/localized-significance-thresholds/final-lst- <br />methodology-document.pdf. <br />12 “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February <br />2015, available at: http://oehha.ca.gov/air/hot_spots/hotspots2015.html <br />13 “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February <br />2015, available at: http://oehha.ca.gov/air/hot_spots/2015/2015GuidanceManual.pdf, p. 8-18 <br />14 “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February <br />2015, available at: http://oehha.ca.gov/air/hot_spots/2015/2015GuidanceManual.pdf, p. 8-6, 8-15