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Section 2 r i0tt ( i, i i r,wn, i , i �i t , - ,i, - o -i ; : r,, , , <br />(DOT/FRA/ORD-12/15, September, 2012) provides the basic guidance and procedures for the assessment <br />of potential noise and vibration impacts from proposed high-speed ground transportation projects. This <br />manual is intended for projects with train speeds of 90 to 250 mph. The manual is similar to the FTA Transit <br />Noise and Vibration Impact Assessment manual (which is intended for projects with train speeds up to 90 <br />mph). An important characteristic of the noise from high-speed trains that is absent from the DEIS noise <br />analysis is analysis of the onset rate of the sound signature. Onset rate is the average rate of change of <br />increasing sound pressure level in decibels per second during a single noise event. The rapid approach of a <br />high-speed train is accompanied by a sudden increase in noise for a receiver near the tracks. Based on the <br />absence of discussion of onset rate and use of the FTA manual figure showing typical A -weighted maximum <br />sound levels instead of the FRA manual showing typical A -weighted levels of high-speed train sources, <br />indicates that the noise analysis relies more on the FTA manual than the more pertinent FRA high-speed <br />train noise manual. <br />The DEIS lacks calculation details and quantitative support for its impact assessment as required by the <br />Federal Railroad Administration manual. In general, the impact assessments are lacking calculation details and <br />quantitative support. The Proposed Project is well beyond the initial planning stages. Therefore, these <br />calculations and support documentation should be required as part of the DEIS analysis. <br />The DEIS fails to include an evaluation of noise and vibration impacts on subterranean archaeological sites <br />and vertical historical sites along the N -S Corridor. The FRA manual references Section 106 and states with <br />regard to historic and archaeological sites, "Special protection provided by law. Section 4(f) of the DOT Act <br />and Section 106 of the National Historic Preservation Act come into play frequently during the <br />environmental review of transit projects. Section 4(f) protects historic sites and publicly -owned parks, <br />recreation areas and wildlife refuges. Section 106 protects historic and archaeological resources." The DEIS <br />does not include a complete list of the subterranean archaeological sites and vertical historical sites along <br />the N -S Corridor. It therefore does not evaluate the Proposed Project's noise and vibration impacts on the <br />subterranean archaeological sites and vertical historical sites along the N -S Corridor. <br />Moreover, AAF made no attempt to collect representative noise data at a representative sampling of <br />intersections along the corridor, as is required by Section 106 of the NHPA. <br />Specifically, CDM Smith noted the following deficiencies: <br />The DEIS relied on an inaccurate methodology for determining existing noise levels. The FRA manual <br />recommends that noise be considered in terms of divergence, absorption/diffusion and/or shielding at <br />a distance of 50 feet from the source. Existing noise levels at 50 feet were not monitored in the field, <br />but rather estimated based on the FTA Guidance Manual based on population density or proximity to <br />an interstate highway, airport, or an existing rail line. No figures are presented to show the existing <br />ambient noise levels in the Project Study Area derived from these different estimated noise levels. <br />Existing ambient noise levels would be helpful in comparing existing and future build impacts at <br />sensitive land uses and historic properties. Measurements of existing ambient noise levels, especially <br />at sensitive land uses and historic properties, should have been used as the combination of various <br />transportation and urban noise sources can be complex. See Appendix B of the FRA manual which <br />discusses options for determination of existing noise levels ranging from full measurement (more <br />accurate) to tabular lookup (less accurate). <br />2-4 3 0 ► 3 Smith <br />