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3.0 ENVIRONMENTAL CHECKLIST <br />The project conforms to applicable control measures from the plan and does not <br />disrupt or hinder the implementation of any Clean Air Plan control measures. <br />The primary goals of the Clean Air Plan are compliance with the state (California) and <br />national ambient air quality standards. As discussed in checklist item b) below, the <br />project's emissions are below all of the thresholds of significance listed in Table 2-1 of the <br />BAAQMD's (2017a) CEQA Guidelines for short-term construction emissions and the project <br />meets all of the screening criteria listed in Table 3-1 of the BAAQMD's (2017a) CEQA Air <br />Quality Guidelines for long-term operational emissions. The thresholds of significance and <br />screening criteria provide a conservative indication of whether the proposed project <br />could result in potentially significant air quality impacts. Therefore, the project would <br />support the primary goals of the Clean Air Plan. <br />BAAQMD air quality planning control measures are developed, in part, based on the <br />emissions inventories contained in the Clean Air Plan, which are derived from projected <br />population growth and VMT for the region. These inventories are largely based on the <br />predicted growth identified in regional and community general plans, including <br />associated development projects. Projects that result in an increase in population or <br />employment growth beyond that identified in regional or community plans could result in <br />increases in VMT and subsequently increase mobile source emissions. As discussed in <br />subsection 3.16, Transportation/Traffic, the project would generate fewer daily trips than <br />the existing medical office buildings on the project site. In addition, the project has been <br />evaluated for consistency with the GreenTRIP program and awarded conditional <br />GreenTRIP certification. The GreenTRIP analysis concluded that project residents would <br />drive 33 miles per day per household, which is 34 percent less than the Bay Area regional <br />average (Rizzo 2018). Therefore, the project would not result in increased regional VMT and <br />would not conflict with or obstruct implementation of the applicable air quality plan. This <br />impact would be less than significant. <br />b) Less Than Significant Impact with Mitigation Incorporated. <br />Short -Term Construction Period Emissions <br />The project would generate short-term criteria air pollutant and ozone precursor emissions <br />from construction activities such as demolition, site grading, asphalt paving, building <br />construction, and architectural coatings (e.g., painting). Common sources of construction <br />emissions include fugitive dust from soil disturbance, fuel combustion from mobile heavy- <br />duty diesel and gasoline -powered equipment, portable auxiliary equipment, and worker <br />commute trips. During construction, fugitive dust, the predominant source of PM,o and <br />PM2.5 emissions, would be generated when wheels or blades disturb surface materials. <br />Uncontrolled dust from construction can become a nuisance and potential health hazard <br />to those living and working nearby. Demolition can also generate fugitive dust PM10 and <br />PM2.5 emissions. Off -road construction equipment is often diesel -powered and can be a <br />substantial source of NOX emissions, in addition to exhaust PMio and exhaust PM2.5 <br />emissions. Worker commute trips, material hauling trips, and architectural coatings are <br />dominant sources of ROG emissions. Predicted unmitigated maximum daily construction - <br />generated emissions for the project are summarized in Table 3.3-4. <br />1388 Bancroft Avenue Project <br />Initial Study/Mitigated Negative Declaration <br />City of San Leandro <br />November 2018 <br />3.0-16 <br />