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traffic analysis prepared for this project, and default and SJVAPCD-recommended model settings and parameters <br /> attributable to construction period and site location. <br /> Table 4.3-7 summarizes the modeled project-generated,operation-related(regional) emissions of criteria air <br /> pollutants and precursors from area and mobile sources. Refer to Appendix B for detailed modeling input <br /> parameters and results. <br /> Total Emissions <br /> Based on the modeling conducted,operation-related activities would not result in total project-generated emissions of <br /> ROG or NOx that exceed SJVAPCD's significance threshold of 10 tpy(refer to Table 4.3-7). Thus,project- <br /> generated,operation-related emissions of criteria air pollutants and precursors would not violate or contribute <br /> substantially to an existing or projected air quality violation,expose sensitive receptors to substantial pollutant <br /> concentrations,or conflict with air quality planning efforts.As a result,this impact would be less than significant. <br /> IMPACT Air Quality—Exposure of Sensitive Receptors to Toxic Air Contaminant Emissions. The project would <br /> 4.3-3 not expose sensitive receptors to substantial emissions of TACs because construction emissions would be <br /> temporary and would rapidly dissipate with distance from the source and proposed operations would not <br /> result in the exceedance of the SJVAPCD's screening criteria for project's resulting in significant TAC <br /> emissions. As a result, this impact would be less than significant. <br /> The exposure of sensitive receptors from on-site project-generated construction-related and operation-related <br /> sources is discussed separately below. <br /> On-Site Construction-Related Equipment Emissions <br /> Construction-related activities would result in short-term project-generated emissions of diesel PM from the <br /> exhaust of off-road heavy-duty diesel equipment for site preparation(e.g., excavation, grading, and clearing); <br /> paving; application of architectural coatings; and other miscellaneous activities. Diesel PM was identified as a <br /> TAC by ARB in 1998. The potential cancer risk from the inhalation of diesel PM, as discussed below, outweighs <br /> the potential noncancer health impacts (ARB 2003). At this time, SJVAPCD has not adopted a methodology for <br /> analyzing such impacts and does not recommended the completion of health risk assessments (HRAs) for <br /> construction-related emissions of TACs,with a few exceptions(e.g.,where construction phase is the only phase <br /> of project) (Reed,pers. comm.,2007). <br /> It is important to note that construction equipment emissions would be reduced over the period of project <br /> development. In January 2001, EPA promulgated a Final Rule to reduce emission standards for 2007 and <br /> subsequent model year heavy-duty diesel engines. These emission standards represent a 90%reduction in NOx, <br /> 72%reduction of nonmethane hydrocarbon(NMHC)emissions, and 90%reduction of PM emissions in <br /> comparison to the 2004 model year emission standards. In December 2004,ARB adopted a fourth phase of <br /> emission standards (Tier 4)in the Clean Air Non-road Diesel Rule that are nearly identical to those finalized by <br /> EPA on May 11,2004.As such, engine manufacturers are now required to meet after treatment-based exhaust <br /> standards NOx and PM starting in 2011 that are more than 90%lower than current levels,putting emissions from <br /> off-road engines virtually on par with those from on-road heavy-duty diesel engines. <br /> More specifically,the dose to which receptors are exposed is the primary factor used to determine health risk(i.e., <br /> potential exposure to TAC emission levels that exceed applicable standards). Dose is a function of the <br /> concentration of a substance or substances in the environment and the duration of exposure to the substance. Dose <br /> is positively correlated with time,meaning that a longer exposure period would result in a higher exposure level <br /> for the maximally exposed individual. Thus,the risks estimated for a maximally exposed individual are higher if a <br /> fixed exposure occurs over a longer period of time. According to the Office of Environmental Health Hazard <br /> Assessment,health risk assessments,which determine the exposure of sensitive receptors to TAC emissions, <br /> Manteca WQCF and Collection System Master Plans EIR EDAW <br /> City of Manteca 4.3-23 Air Quality <br />