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4.8 Nolse <br />threshold for people in the vicinity of the project site. Groundborne -vibration resulting from operation <br />of the proposed project would primarily be generated by trucks making periodic deliveries to the <br />proposed Transit Zoning Code (SD 84A and SD 84B) area. However, these types of deliveries would be <br />consistent with deliveries that are currently made along roadways to commercial uses in the proposed <br />Transit Zoning Code (SD 84A and SD 84B) area and in the proposed project vicinity and would not <br />increase groundborne vibration above existing levels. Because no substantial sources of groundborne <br />vibration would be built as part of the proposed project, no vibration impacts would occur during <br />operation of the proposed project. Therefore, operation of the proposed project would not expose <br />sensitive receptors on or off site to excessive groundborne vibration or groundborne noise levels, and <br />this impact would be less than significant. <br />Impact 4.8-4 Operation of the Southern California Regional Rail Authority's rail line <br />would not generate and expose sensitive receptors located within the <br />Transit Zoning Code (SD 84A and SD 8413) area to excessive groundborne <br />vibration or groundborne noise levels. This is considered a less -than - <br />significant impact. <br />Implementation of the Transit Zoning Code (SD 84A and SD 84B) would locate new sensitive land uses <br />within the vicinity of the existing railroad tracks. Problems for residential uses, such as disturbance due to <br />groundborne vibration from these sources, are usually contained to areas with n about 200 feet of the <br />vibration source (HMMII2006). Typically, the main effect of groundborne vibration is to cause <br />annoyances for occupants of nearby buildings. The proposed residential uses in the Logan <br />Neighborhood, Transit Village, and First Street Corridor could be located within 200 feet from the <br />centerline of the railroad. As discussed earlier, trains typically produce a vibration level of 75 VdB at a <br />distance of 50 feet from the tracks during operation and 65 dBA at a distance of 50 feet while stopped at <br />a train station, both of which are below the human annoyance threshold of 85 VdB. Therefore, the <br />occupants of the proposed residential units would not be exposed to potentially significant vibration <br />levels, and th s impact would be less than significant. <br />Threshold Would the project result in a substantial temporary or periodic increase in ambient <br />noise levels in the project vicinity above levels existing without the project? <br />Impact 4.8-5 Construction activities associated with the proposed project would result in <br />a substantial temporary or periodic increase in ambient noise levels. <br />However, the project's construction noise impacts would be temporary, <br />would not occur during recognized sleep hours, and would be consistent <br />with the exemption for construction noise that exists in the Municipal <br />Code. Therefore, this impact would be considered less than significant. <br />As discussed in Impact 4.8-1, construction activities associated with the proposed project could reach <br />above 86 dBA Leg within 50 feet of the proposed project site. These construction activities would <br />represent a substantial temporary or periodic increase in ambient noise levels. As discussed previously <br />under "Thresholds of Significance," this analysis assumes that an increase of 5.0 dBA or greater over <br />ambient noise levels is substantial and significant. As shown in Table 4.8-3, the highest existing daytime <br />ambient noise level monitored in the project vicinity was 77.0 dBA Leg at the Rail Station Platform. As <br />City of Santa Ana Transit Zoning Code (SD 84A and SD 848) EIR 4.8-25 <br />