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localized standards for receptors that are within 25 meters of the Project's construction activities. <br />Additionally, the Project would be required to implement applicable mitigation measures from the <br />Certified EIR that would further reduce the Project's emission, which would not exceed <br />SCAQMD's thresholds. Therefore, based on SCAQMD guidance, localized emissions of criteria <br />pollutants would not have the potential to expose sensitive receptors to substantial concentrations <br />that would present a public health concern. <br />The primary toxic air contaminant TAC that would be generated by construction activities is diesel <br />particulate matter (PM), which would be released from the exhaust stacks of construction equipment. <br />The construction emissions modeling conservatively assumed that all equipment present on the <br />Project Site would be operating simultaneously throughout most of the day, while in all likelihood this <br />would rarely be the case. Average daily emissions of diesel PM would be less than one pound per <br />day throughout the course of Project construction. Therefore, the magnitude of daily diesel PM <br />emissions, would not be sufficient to result in substantial pollutant concentrations at off -site locations <br />nearby. <br />Furthermore, according to SCAQMD methodology, health risks from carcinogenic air toxics are <br />usually described in terms of individual cancer risk. "Individual Cancer Risk" is the likelihood that a <br />person exposed to concentrations of TACs over a 30-year period will contract cancer based on the <br />use of standard risk -assessment methodology. The entire duration of construction activities <br />associated with implementation of the Project is anticipated to be approximately 36 months, and the <br />magnitude of daily diesel PM emissions will vary over this time period. No residual emissions and <br />corresponding individual cancer risk are anticipated after construction. Because there is such a short- <br />term exposure period, construction TAC emissions would result in a less than significant impact. Thus, <br />construction of the Project would not expose sensitive receptors to substantial diesel PM <br />concentrations. Therefore, no new or increased significant impacts would occur beyond the air <br />quality impacts already identified in the Certified EIR. <br />Operational Emissions <br />The Project Site would be redeveloped with multi -family residences, retail, and office uses, land <br />uses that are not typically associated with TAC emissions. Typical sources of acutely and <br />chronically hazardous TACs include industrial manufacturing processes (e.g., chrome plating, <br />electrical manufacturing, petroleum refinery). The Project would not include these types of <br />potential industrial manufacturing process sources. It is expected that quantities of hazardous <br />TACs generated on -site (e.g., cleaning solvents, paints, landscape pesticides) for the types of <br />proposed land uses would be below thresholds warranting further study under California <br />Accidental Release Program. <br />When considering potential air quality impacts under CEQA, consideration is given to the location <br />of sensitive receptors within close proximity of land uses that emit TACs. CARB has published <br />and adopted the Air Quality and Land Use Handbook: A Community Health Perspective, which <br />provides recommendations regarding the siting of new sensitive land uses near potential sources <br />of air toxic emissions (e.g., freeways, distribution centers, rail yards, ports, refineries, chrome <br />plating facilities, dry cleaners, and gasoline dispensing facilities). The SCAQMD adopted similar <br />recommendations in its Guidance Document for Addressing Air Quality Issues in General Plans <br />Cabrillo Town Center City of Santa Ana <br />Technical Memorandum August 2023 <br />City Council 18 — 514 10/3/2023 <br />