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6 - GPA19-01; AA19-01_651 W SUNFLOWER AVENUE
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6 - GPA19-01; AA19-01_651 W SUNFLOWER AVENUE
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<br />Legacy Sunflower Apartments Page 45 <br />Mitigated Negative Declaration – March 14, 2019 <br /> <br />Operations-Related Local Air Quality Impacts <br /> <br />Project-related air emissions may have a potential to exceed the State and Federal air quality <br />standards in the project vicinity, even though the pollutant emissions may not be significant to create a <br />regional impact to the SCAB. The project was analyzed for potential local CO emission impacts from <br />project-generated vehicular trips and on-site operations. <br /> <br />Local CO Emission Impacts from Project-Generated Vehicular Trips <br /> <br />CO is the pollutant of major concern along roadways because the most notable source of CO is the <br />operation of motor vehicles. For this reason, CO concentrations are usually indicative of the local air <br />quality generated by a roadway network and are used as an indicator of potential local air quality <br />impacts. <br /> <br />To determine if the project could generate emission levels in excess of the CO standards, a sensitivity <br />analysis is typically conducted to determine the potential for CO “hot spots” at intersections in the <br />general project vicinity. Because of reduced speeds and vehicle queuing, “hot spots” potentially can <br />occur at high traffic volume intersections with a Level of Service E or worse. <br /> <br />The intersection in the project area with the highest traffic volume is Bristol Street at Anton Boulevard <br />with an evening peak hour volume of 2,203 trips (Year 2040 Buildout Plus Project). The 1992 Federal <br />Attainment Plan for Carbon Monoxide (1992 CO Plan) showed that an intersection with a daily traffic <br />volume of approximately 100,000 vehicles per day would not violate the CO standard. Therefore, as <br />the intersection with the highest traffic volume falls far short of 100,000 vehicles, no CO “hot spot” <br />modeling was performed for the project. As a result, the project would not have any significant long- <br />term CO emission impact to local air quality. <br /> <br />Local Air Quality Impacts from On-Site Operations <br /> <br />Project-related air emissions from on-site sources such as architectural coatings, the operation of <br />landscape equipment, on-site usage of natural gas appliances and the operation of vehicles on-site <br />may have the potential to exceed the State and Federal air quality standards in the project vicinity, even <br />though these pollutant emissions may not be significant enough to create a regional impact to the Air <br />Basin. <br /> <br />According to SCAQMD LST methodology, LSTs would apply to the operational phase of a project, if the <br />project includes stationary sources, or attracts mobile sources (such as heavy-duty trucks) that may <br />spend long periods queuing and idling at the site; such as industrial warehouse/transfer facilities. The <br />project is a multi-family attached residential project and does not include such uses. Therefore, due the <br />lack of stationary source emissions, no long-term localized significance threshold analysis is warranted. <br /> <br />The project would not generate any air emissions that exceed SCAQMD thresholds. The elementary <br />school and the residential development west, south and east of the project, respectively, are <br />considered sensitive land uses. Because the project would not generate any air emissions that exceed <br />adopted emission thresholds, the sensitive receptors adjacent to the project would not be exposed to <br />substantial pollutant concentrations. Construction and long-term operational emissions by the project <br />would not significantly impact any sensitive receptors adjacent to or in the project vicinity. <br /> <br /> <br />6-67
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