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Response to Comment <br /> <br /> <br /> <br />City of Santa Ana 12 <br />Magnolia at the Park Multi-Family Residential Project December 2018 <br />are designed to encompass the spectrum of potential meteorological conditions - not actual measured data; calculation <br />of only a one-hour concentration for each of the theoretical meteorological conditions; and no differentiation is provided <br />between daytime and nighttime conditions. As such, the model calculates one-hour concentrations under all conditions. <br />Due to its simplicity and reliance on limited actual site-specific physical and meteorological conditions, AERSCREEN <br />provides an overstated assessment of pollutant concentrations. Given the limited TAC emissions sources that would <br />result from operation of the project, the assessment provided in this comment has greatly exaggerated and <br />overestimated project operational risk impacts, and therefore is not substantial evidence of an actual project impact. <br /> <br />As detailed in the previous responses, both construction and operational emissions resulting from the project would be <br />below SCAQMD thresholds with implementation of Mitigation Measure AQ-1. For these reasons, health risk impacts <br />at adjacent sensitive receptors would be less than significant and would not result in a potential impact not previously <br />addressed in the EIR. <br /> <br />Comment 30: This comment states that the screening‐level HRA, provided as Comment 29, is conservative and its <br />purpose is to determine if a more refined HRA needs to be conducted. The comment asserts that based on the results <br />of the screening-level HRA provided as Comment 29, refined construction and operational HRAs need to be prepared <br />to examine air quality impacts generated by project construction and operation using site‐specific information. The <br />comment further asserts that an updated analysis of the project’s health risk impact should be prepared and mitigation <br />measures included to reduce impacts to a less‐than‐significant level. <br /> <br />Response 30: Refer to Responses 27 through 29. Project specific analysis of potential air quality impacts have been <br />completed pursuant to the SCAQMD methodology, which has determined that impacts would be less than significant <br />with Mitigation Measure AQ-1 related to off-road diesel construction equipment compliance with EPA/CARB Tier 3 <br />emissions standards. An updated analysis and additional mitigation measures are not required. <br /> <br />Comment 31: This comment provides a list of recommended mitigation measures to reduce diesel particulate matter <br />emissions that is emitted by on‐road vehicles and by off‐road construction equipment. <br /> <br />Response 31: As described by Response 30, impacts would be less than significant with Mitigation Measure AQ-1 <br />and additional mitigation measures, including those listed in this comment, are not required. <br /> <br />Comment 32: This comment states that the recommended mitigation measures offer a cost‐effective, feasible way to <br />incorporate lower‐emitting design features into the project, and that an updated EIR needs be prepared to additional <br />analyses and include diesel particulate matter related mitigation measures to reduce health risk impacts to a less than <br />significant level. <br /> <br />Response 32: As described by Response 30, impacts would be less than significant with Mitigation Measure AQ-1 <br />and additional mitigation measures, including those listed in this comment, are not required. <br /> <br /> <br /> <br /> <br />2-308