Final FONSI and EA for hot cargo pad on Kirtland AFB - Kirtland Air ...
Final FONSI and EA for hot cargo pad on Kirtland AFB - Kirtland Air ...
Final FONSI and EA for hot cargo pad on Kirtland AFB - Kirtland Air ...
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<str<strong>on</strong>g>Final</str<strong>on</strong>g> <str<strong>on</strong>g>EA</str<strong>on</strong>g> Addressing C<strong>on</strong>structi<strong>on</strong>, Operati<strong>on</strong>, <str<strong>on</strong>g>and</str<strong>on</strong>g> Maintenance of a Hot Cargo Pad<br />
4.2 Noise<br />
4.2.1 Evaluati<strong>on</strong> Criteria<br />
Noise impact analyses typically evaluate potential changes to the existing noise envir<strong>on</strong>ment that would<br />
result from implementati<strong>on</strong> of a proposed acti<strong>on</strong>. Potential changes in the acoustical envir<strong>on</strong>ment can be<br />
beneficial (i.e., if they reduce the number of sensitive receptors exposed to unacceptable noise levels or<br />
reduce the ambient sound level), negligible (i.e., if the total number of sensitive receptors to unacceptable<br />
noise levels is essentially unchanged), or adverse (i.e., if they result in increased sound exposure to<br />
unacceptable noise levels or ultimately increase the ambient sound level). Projected noise effects were<br />
evaluated qualitatively <str<strong>on</strong>g>for</str<strong>on</strong>g> the alternatives c<strong>on</strong>sidered.<br />
4.2.2 Envir<strong>on</strong>mental C<strong>on</strong>sequences<br />
4.2.2.1 Proposed Acti<strong>on</strong><br />
The Proposed Acti<strong>on</strong> includes the c<strong>on</strong>structi<strong>on</strong> of a new <str<strong>on</strong>g>hot</str<strong>on</strong>g> <str<strong>on</strong>g>cargo</str<strong>on</strong>g> <str<strong>on</strong>g>pad</str<strong>on</strong>g>, including the associated taxiway,<br />
<str<strong>on</strong>g>and</str<strong>on</strong>g> demoliti<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> repair of the taxiway to the existing <str<strong>on</strong>g>hot</str<strong>on</strong>g> <str<strong>on</strong>g>cargo</str<strong>on</strong>g> <str<strong>on</strong>g>pad</str<strong>on</strong>g> (Pad 5) as discussed in Secti<strong>on</strong><br />
2.1.1. Noise from demoliti<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> c<strong>on</strong>structi<strong>on</strong> activities would vary depending <strong>on</strong> the type of equipment<br />
being used, the area the activity would occur in, <str<strong>on</strong>g>and</str<strong>on</strong>g> the distance of the activity from the noise source. To<br />
predict how c<strong>on</strong>structi<strong>on</strong> activities would impact adjacent populati<strong>on</strong>s, noise from the probable<br />
c<strong>on</strong>structi<strong>on</strong> was estimated. For example, as shown in Table 3-2, c<strong>on</strong>structi<strong>on</strong> usually involves several<br />
pieces of equipment (e.g., dump truck <str<strong>on</strong>g>and</str<strong>on</strong>g> paver) that can be used simultaneously. Under the Proposed<br />
Acti<strong>on</strong>, the cumulative noise from the c<strong>on</strong>structi<strong>on</strong> equipment, during the busiest day, was estimated to<br />
determine the total impact of noise from c<strong>on</strong>structi<strong>on</strong> activities at a given distance. Examples of expected<br />
cumulative demoliti<strong>on</strong> noise during daytime hours at specified distances are shown in Table 4-1. These<br />
sound levels were predicted at 100, 200, 400, 800, <str<strong>on</strong>g>and</str<strong>on</strong>g> 1,200 feet from the source of the noise.<br />
Table 4-1. Predicted Noise Levels from Demoliti<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> C<strong>on</strong>structi<strong>on</strong> Activities<br />
Distance from Noise Source<br />
Predicted Noise Level<br />
100 feet 86 dBA<br />
200 feet 80 dBA<br />
400 feet 74 dBA<br />
800 feet 68 dBA<br />
1,200 feet 64 dBA<br />
The proposed <str<strong>on</strong>g>hot</str<strong>on</strong>g> <str<strong>on</strong>g>cargo</str<strong>on</strong>g> <str<strong>on</strong>g>pad</str<strong>on</strong>g> would fall within the DNL 65 to 69 dBA noise c<strong>on</strong>tours, <str<strong>on</strong>g>and</str<strong>on</strong>g> the proposed<br />
taxiway would fall within the DNL 70 to 74 dBA noise c<strong>on</strong>tours from aircraft operati<strong>on</strong>s at Albuquerque<br />
Internati<strong>on</strong>al Sunport. Since multiple single noise events create the cumulative DNL value, the actual<br />
sound levels that a pers<strong>on</strong> hears within the area of the DNL noise c<strong>on</strong>tours fluctuates throughout a 24-<br />
hour period. C<strong>on</strong>sequently, populati<strong>on</strong>s within <str<strong>on</strong>g>and</str<strong>on</strong>g> adjacent to the Proposed Acti<strong>on</strong> are accustomed to<br />
fluctuati<strong>on</strong>s of noise levels in the 70 to 90 dBA range. Noise generati<strong>on</strong> would last <strong>on</strong>ly <str<strong>on</strong>g>for</str<strong>on</strong>g> the durati<strong>on</strong><br />
of c<strong>on</strong>structi<strong>on</strong> activities <str<strong>on</strong>g>and</str<strong>on</strong>g> would be isolated to normal working hours (i.e., between 7:00 a.m. <str<strong>on</strong>g>and</str<strong>on</strong>g> 5:00<br />
p.m.). C<strong>on</strong>sequently, demoliti<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> c<strong>on</strong>structi<strong>on</strong> activities from the Proposed Acti<strong>on</strong> would result in<br />
impacts <strong>on</strong> the noise envir<strong>on</strong>ment; however, these impacts would be expected to be less than significant.<br />
Kirtl<str<strong>on</strong>g>and</str<strong>on</strong>g> <strong>AFB</strong>, NM January 2011<br />
4-3