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Hana Japan Restaurant Project <br />Initial Study/Mitigated Negative Declaration <br />21 <br />May 2025 <br />Table 3 <br />Unmitigated Maximum Operational Emissions <br />Pollutant <br />Proposed Project <br />Emissions <br />Threshold of <br />Significance Exceeds <br />Threshold? lbs/day tons/yr lbs/day tons/yr <br />ROG 2.15 0.31 54 10 NO <br />NOX 2.09 0.24 54 10 NO <br />PM10* 3.72 0.35 82 15 NO <br />PM2.5* 0.97 0.09 54 10 NO <br />* Emissions from exhaust only. BAAQMD has not yet adopted thresholds for fugitive PM emissions. <br /> <br />Source: CalEEMod, March 2025 (see Appendix A). <br /> <br />Cumulative Emissions <br />Past, present, and future development projects contribute to the region’s adverse air <br />quality impacts on a cumulative basis. By nature, air pollution is largely a cumulative <br />impact. A single project is not sufficient in size to, by itself, result in nonattainment of <br />AAQS. Instead, a project’s individual emissions contribute to existing cumulatively <br />significant adverse air quality impacts. If a project’s contribution to the cumulative impact <br />is considerable, then the project’s impact on air quality would be considered significant. In <br />developing thresholds of significance for air pollutants, BAAQMD considered the emission <br />levels for which a project’s individual emissions would be cumulatively considerable. The <br />thresholds of significance presented in Table 1 represent the levels at which a project’s <br />individual emissions of criteria air pollutants or precursors would result in a cumulatively <br />considerable contribution to the SFBAAB’s existing air quality conditions.7 If a project <br />exceeds the significance thresholds presented in Table 1, that project’s emissions would <br />be cumulatively considerable, resulting in significant adverse cumulative air quality <br />impacts to the region’s existing air quality conditions. <br /> <br />As presented above, the proposed project would not exceed the applicable thresholds for <br />criteria pollutant emissions during project construction or operations. Thus, the project <br />would not result in a cumulatively considerable contribution to the region’s existing air <br />quality conditions. <br /> <br />Conclusion <br />As stated previously, the applicable regional air quality plans include the 2001 Ozone <br />Attainment Plan and the 2017 Clean Air Plan. Because the proposed project would not <br />result in operational emissions of criteria pollutants in excess of BAAQMD’s applicable <br />threshold of significance, conflicts with or obstruction of implementation of the applicable <br />regional air quality plans would not occur. Thus, a less-than-significant impact would <br />result. <br /> <br />c. Some land uses are considered more sensitive to air pollution than others, due to the <br />types of population groups or activities involved. Heightened sensitivity may be caused by <br />health problems, proximity to the emissions source, and/or duration of exposure to air <br />pollutants. Children, pregnant women, the elderly, and those with existing health problems <br />are especially vulnerable to the effects of air pollution. Sensitive receptors are typically <br />defined as facilities where sensitive receptor population groups (i.e., children, the elderly, <br /> <br />7 Bay Area Air Quality Management District. California Environmental Quality Act Air Quality Guidelines [pg. 2-1]. <br />May 2017.