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<br />The Bowery Mixed-Use Project CEQA Findings of Fact <br /> <br />City of Santa Ana 29 <br />May 2020 <br /> <br />As shown on Draft EIR Table 5.10-6, construction noise at the nearby receiver locations would range <br />from 51.0 to 71.4 dBA Leq, which would not exceed the 85 dba Leq daytime construction noise level <br />threshold (the National Institute for Occupational Safety and Health (NIOSH) Criteria for <br />Recommended Standard: Occupational Noise Exposure) at nearby non-residential non-sensitive <br />receiver locations. Therefore, construction impacts would be less than significant. <br /> <br />Also, the increase in temporary noise from Project construction, as detailed in Draft EIR Table 5.10- <br />7, would not exceed the 12 dBA Leq significance threshold (per Caltrans Traffic Noise Analysis <br />Protocol). Therefore, impacts related to substantial increases in ambient noise related to construction <br />activity would be less than significant. <br /> <br />Operation <br />Onsite Operational Noise. Noise generated by the Project site would occur from stationary <br />equipment such as heating, ventilation, and air conditioning (HVAC) units that would be installed for <br />the new development, use of parking facilities, trash removal activity, and activity at outdoor <br />gathering areas. Based on these typical noise levels, operation of the Project would not result in an <br />exceedance of the City’s Municipal Code Section 18-313 noise standards. Also, the City’s building <br />and plan check permitting process includes verification that the location of operational noise sources <br />would not result in an exceedance of the municipal code standards. Thus, the City’s standards <br />development permitting process would ensure that the proposed Project would not generate on-site <br />operational noise that would exceed noise standards. Therefore, impacts would be less than <br />significant. <br /> <br />Onsite Traffic Noise. The location and design of the multi-family residential outdoor common areas <br />substantially limits the exposure to traffic noise. As shown on Draft EIR Table 5.10-8, the exterior <br />noise levels at the multi-family residential outdoor common areas would range from 45.1 to 57.7 <br />dBA CNEL, which is below the General Plan Noise Element 65 dBA CNEL exterior noise level <br />standard for outdoor common areas. Therefore, the on-site traffic noise impacts at the multi-family <br />residential outdoor common areas would be less than significant. <br /> <br />Offsite Traffic Noise. In the existing with Project conditions (Draft EIR Table 5.10-9) noise would <br />range from 66.8 to 75.8 dBA CNEL. Implementation of the proposed Project A would generate a <br />noise level increase of up to 0.5 dBA CNEL on the study area roadway segments, which is less than <br />the 1.5 dBA CNEL threshold for areas above 65 dBA CNEL. Thus, off-site traffic noise impacts in <br />the existing plus Project condition would be less than significant. <br /> <br />In the opening year (2022) with Project conditions (Draft EIR Table 5.10-10) noise would range <br />from 67.4 to 76.2 dBA CNEL. Implementation of the proposed Project would generate a noise level <br />increase of up to 0.5 dBA CNEL on the study area roadway segments, which is less than the 1.5 <br />dBA CNEL threshold for areas above 65 CNEL. Thus, off-site traffic noise impacts in the opening <br />year plus Project condition would be less than significant. <br /> <br />In 2040 with Project conditions (Draft EIR Table 5.10-11) noise would range from 69.7 to 76.6 dBA <br />CNEL. Implementation of the proposed Project would generate a noise level increase of up to 0.4 <br />dBA CNEL on the study area roadway segments, which is less than the 1.5 dBA CNEL threshold for <br />areas above 65 CNEL. Thus, off-site traffic noise impacts in the 2040 plus Project condition would <br />be less than significant. <br /> <br />3-51