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3. Environmental Checklist <br />complies with the goals of the 2017 Clean Air Plan. Specifically, the Proposed Project would promote <br />Natural and Working Lands Control Measure NW3 Carbon Sequestration in Wetlands. Accordingly, the <br />Proposed Project would result in beneficial impacts associated with implementation of provisions of a <br />local air quality plan, qualifying as No Impact in relation to the identification of significant impacts <br />under CEQA. <br />Impact Designation: No Impact <br />b) Increase of any criteria pollutant for which the Project region is not attaining: Implementation of the <br />Proposed Project would result in conversion of the existing 6.9-acre wastewater storage basin into a <br />treatment wetland facility. Construction would occur over five phases, with two concurrent phases <br />(refer to Section 2.4). Operation of the Proposed Project would require some maintenance activities <br />but would not require additional employees. According to the BAAQMD's 2022 Air Quality Guidelines, <br />for a project that requires simultaneous occurrence of two or more construction phases, a detailed <br />assessment must be performed. Therefore, the Proposed Project -related emissions were calculated <br />using the California Emissions Estimator Model (CaIEEMod) version 2022.1.16 In accordance with <br />guidance provided in Appendix D of the 2022 Air Quality Guidelines, irrigated areas are assessed as <br />City Park Land Use Type within CaIEEMod. The Proposed Project consists of a project similar to an <br />irrigated lands project and was identified as a City Park. Defaults within CaIEEMod were adjusted to <br />account for the Project specific details related to construction and operation of the Proposed Project <br />versus a typical City Park. Construction and operation emissions would not overlap; therefore, <br />construction and operation emissions are analyzed separately. It was assumed that construction <br />would last approximately three months starting July 1st, 2024. All CaIEEMod data tables, including <br />input values, assumptions used, and output values, are detailed in Appendix A. <br />Construction lmgacts <br />To estimate criteria emissions from construction equipment, anticipated construction equipment and <br />anticipated personnel vehicle trips for each of the five construction phases were input over defaults <br />using information provided by Project engineers. Based on the schedule and construction <br />progression, Phases 1 and 2 were assumed to overlap. Approximately 11,000 cubic yards of fill would <br />be required during Phase I grading and no export of soil would be necessary to develop the Proposed <br />Project. Demolition was selected as part of Phase I to account for the removal of existing concrete <br />debris from existing soil stockpiles on site. According to engineering calculations, it was estimated <br />approximately 6000 tons of debris would be removed from the site to provide clean fill from the on - <br />site stockpile. The Proposed Project would result in the temporary generation of ROG, NOx, PM10, and <br />other regulated pollutants during construction. ROG and NOx emissions are associated with personnel <br />vehicle trips, delivery of materials, and construction equipment exhaust. PM10 is generated during <br />site preparation, excavation, road paving, and from exhaust associated with construction equipment. <br />Resulting emissions from the Proposed Project are presented in Table 3-4 and compared to the <br />BAAQMD significance thresholds to assess CEQA impacts. As shown in Table 3-4, emissions from the <br />is California Air Pollution Officers Association (CAPCOA) in collaboration with the California Air Districts. California Emissions Estimator <br />Model (CaIEEMod) (Version 2022.1.1.21). Available at:: tllu5:ri ivww ssCL1 �. _ 1 nnti ad nE + .,i <br />San Leandro Treatment Wetlana 11 <br />IS/MND <br />