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CO, Five, and PMb. remissions, which are collectively referred to as criteria air pollutants,° 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. Asa result, hea It impacts from exposure to toxic air contaminants <br />(TACs), such as diesel particulate matter (DPM), were not analyzed, thus leaving 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 Manua! for Preparation of Health Risk Assessments." 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 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 he evaluated for cancer <br />risks to nearby sensitive receptors." Therefore, per OEH"AS t idelines, 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 along period of time. As previously stated, Project <br />operation will generate approximately 11,546 daily vehicle trips, which will generate additional l exhaust <br />emissions and continue to expose nearby sensitive receptors to DPM emissions (p. 5.14-11, Table 5.14- <br />5). The OEHHA do cum ent recommends that exposure from projects lasting more than 6months 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).1q 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 frmonth 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 Pmject 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 H HA to nearby, existing <br />sensitive receptors as a result of Project construction, the DEIR fails to compare the excess health risk to <br />31 "Final Localized Significance Threshold Method dogy." KAUMD, Revised July 2008, am liable at.- <br />httc;/fw w.agmd.am/dots/defa uIt-source/ceaaNirldbookAacalized-significance-thresholds/final-Ist- <br />methodology document. pdf. <br />11 "Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments " OEHHA, February <br />2015,availabk or: htip;/Icehha.w.gwlafr/hot soots/hotsocts2015.1ttml <br />to "Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments." OEHHA, February <br />2015, available at: hup Vcehha.ca..gcw/afrlhot sootsl2015/2015GuidanceManuai.vdf. p. 8-18 <br />to "Rick Assasvmpat Ci Moline, Guidance Mani al for Prppa ration of Health Risk Assessments"OFHHA, F6hn inry <br />2013, available at: hua Vo hha.ca.cov/afrfhot soots/2015/2015GuidanceManua9.pdf. p. ", 8-15 <br />35 <br />75l77 <br />