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<br />.., <br /> <br />Jeffry S. Rice, AICP <br />City of Santa Ana <br />February 7, 200 I <br />Page 2 <br /> <br />URS <br /> <br />and recommended expanding the discussion of why sound insulation was not considered for <br />"moderately" noise-impacted buildings. <br /> <br />3. The original noise analysis assumed that the CenterLine project would use LRVs with noise <br />characteristics similar to the Tri-Met system in Portland. The SIR DEIS/R has additionally <br />evaluated an alternative technology using the Ansaldo Breda STREAM vehicles. These are also <br />steel-wheel-on-steel-rail technology LRVs that may eliminate the need for catenary masts and <br />wires. The SIR DEIS/R noise analysis assumed that the Breda STREAM vehicle noise emissions <br />would be equivalent to those of the Tri-Met LRVs. While this assumption is reasonable, no data <br />was presented to support the assumption/assertion that the Breda LRVs would produce <br />comparable noise levels. <br /> <br />4. Implementation of the revised Elevated Alternative (EA-2) results in zero residual noise impact <br />to sensitive uses in Santa Ana, assuming inclusion of noise abatement design or mitigation <br />measures. Thus, the EA-2 Alternative would be the environmentally preferred alternative from a <br />noise impact perspective. <br /> <br />5. Vibration impacts for all project alternatives in Santa Ana are mitigable. Reasonable and feasible <br />vibration mitigation methods and actions were described in the DEISIR. However, there was no <br />clear commitment in the DEIS/R to specifically incorporate vibration reduction measures into the <br />project design or adopt them as separate vibration impact mitigation measures. The SIR DEIS/R <br />remains cloudy on this issue of vibration mitigation. <br /> <br />6. With respect to vibration effects, the authors of the SIR DEIS/R based their analysis of impact on <br />what we believe to be an incorrect and unsupportable assertion regarding the FT A's impaci <br />criterion. The authors have arbitrarily used a vibration level two velocity decibels (+2 VdB) <br />above the established FTA impact criterion of 72 VdB for Category 2 uses (primarily residences) <br />exposed to "Frequent Events" (70+ vibration events per day). The author's rationale is that FT A <br />specifies two classes of impact for noise effects. While this is true for noise, thc FT A has <br />adopted criteria levels for various land use types and frequency of events that result in only one <br />specific vibration impact criterion for each set of vibration circumstances. The FT A guidelines <br />do not provide for arbitrary modification of their impact critcria into subclasses. There is no <br />ambiguity regarding vibration impact in our opinion. If the project vibration levels will be below <br />the FT A-specified impact critcrion there will be no impact; if vibration levels are expected to be <br />above the FT A criterion there would be impact and it should be mitigated. Thus, we recommend <br />that the City require I) a clarification of Section 4.10.7 regarding vibration impacts, and 2) a <br />commitment to providing vibration reducing design features or incorporation of mitigation <br />measures as necessary to avoid vibration impact from any selected Alternative. <br /> <br />7. The Rail Systems Specifications, Task 5.], Section]], NOISE AND VIBRATION, contained in <br />Volume II of the SIR DEIS/R (page 89 et. seq.) provide design criteria to avoid adverse effects <br />and significant impacts from noise and vibration arising out of operation of the system including <br /> <br />1':\200 ]\57-0996] 035.02 CcnterLinl.'\rcporLdoc <br />