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0� OCTA I Santa Ana/Garden Grove Fixed Guideway Project <br />Noise and Vibration Technical Analysis Re-evaluation in Support of Minor Design Modifications <br />3 <br />200 <br />3 <br />61 38 <br />64 <br />No Impact <br />4 <br />50 <br />2 <br />62 42 <br />59 <br />No Impact <br />Source: URS (February 2012) and HDR (June 2016). <br />Notes: TPSS#1 and TPSS#4 noise levels are based on an orientation where the HVAC units are located on the <br />opposite side of and directed away from the closest receptors. <br />Land Use Category 2: Residences and buildings where people normally sleep. <br />Land Use Category 3: Institutional land uses with primarily daytime and evening use. <br />FTA Impact Criteria: The noise level below which no impact would occur. Based on the land use category <br />and the existing noise level. <br />No Impact: A proposed project is considered to have no noise impact since, on average, the introduction of <br />the project will result in an insignificant increase in the number of people highly annoyed by the new noise. <br />Moderate Impact: The change in the cumulative noise level is noticeable to most people, but may not be <br />sufficient to cause strong, adverse reactions from the community. <br />Severe Impact: A significant percentage of people would be highly annoyed by the new noise. <br />The City of Santa Ana's Municipal Code noise limit for nighttime activities near sensitive land <br />uses is 50 dBA for events that occur for more than 30 minutes in a one hour period. This limit is <br />reduced by 5 dBA, to 45 dBA, for noise consisting entirely of impact noise, simple tone noise, <br />speech, music, or any combination thereof. TPSS units 1 and 4 are located in residential areas. <br />As the Ldn noise levels listed in Table N are 6 dB higher than the hourly Leq noise level, the <br />TPSS nighttime hourly noise levels would range from 36 to 39 dBA Leq. Therefore, the sensitive <br />land uses located within the vicinity of the proposed TPSS units would not be exposed to noise <br />levels exceeding 45 dBA. However, it is recommended that the following measures be <br />implemented to ensure that the impact is below a level of significance: <br />- Orient the TPSS unit so that the HVAC units, the primary source of noise, are pointing <br />away from the nearest residence. <br />- At the residential locations, the TPSS units will be designed so as not to exceed a <br />maximum noise level of 45 dBA at a distance of 50 feet from the unit or at the setback <br />line of the nearest building, whichever is closer. <br />Conclusions <br />The design modifications that have been determined to potentially affect noise and vibration and <br />were re-evaluated in this memo include both physical improvements (alignment shift, changes <br />to special trackwork, and TPSS repositioning), and operational modifications (increase in speed <br />and traffic signal priority). <br />Streetcar Noise (Operation). The EA identified "severe" operational impacts at five different <br />locations, and "moderate" impacts at seven other locations. Therefore, without mitigation, the <br />project would result in adverse effects related to noise. The EA identified three measures to <br />reduce these impacts: Mitigation Measure N1 would reduce noise impacts associated with <br />warning horns; Mitigation Measure N2 would reduce noise impacts associated with streetcar <br />pass -by noise; and Mitigation Measure N3 would reduce streetcar noise through the placement <br />of noise barriers at certain locations. Based on this re-evaluation of noise analysis, there would <br />be no new adverse or significant noise effect from streetcar operation, nor would there be an <br />15 <br />