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Draft EA - San Diego International Airport

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SAN DIEGO INTERNATIONAL AIRPORT – PROPOSED RUNWAY 9 DISPLACED THRESHOLD<br />

number of annual operations than is now predicted to occur by 2014. However, because the Proposed Action<br />

has no effect on the number or type of aircraft operations at SDIA, nor will it change arrival or departure<br />

routes to the <strong>Airport</strong>, the NEM contours presented in Figure 4-1 provide a reasonable representation of the<br />

noise contours anticipated to be generated by aviation activity at SDIA in the general timeframe of the<br />

Proposed Action.<br />

4.1.2 NO ACTION ALTERNATIVE<br />

The No Action alternative would not affect (increase or decrease) the number of aircraft operations at SDIA or<br />

the routing of aircraft in the air to and from the <strong>Airport</strong>, when compared to the Proposed Action for the same<br />

timeframes. Under the No Action alternative, existing noise levels from aircraft operations would generally<br />

continue, with some change due to the natural growth in aviation activity forecast to occur at the <strong>Airport</strong> with<br />

or without the Proposed Action.<br />

4.1.3 PROPOSED ACTION<br />

The Proposed Action would result in a minor shifting of a portion of the CNEL 65 dB noise contour (see<br />

Figure 4-1). Relocation of the displaced threshold on Runway 9 by 300 feet and reduction of the glide slope<br />

would result in up to an 8-foot shift of the CNEL 65 dB noise contour to the east, but this shift only affects the<br />

western extent of the contour (no change would result for most of the noise contour). Because the prevailing<br />

winds at the <strong>Airport</strong> are from the west, Runway 9 is only utilized for arrivals and departures approximately 5<br />

percent of the year (see Table 4-1). The Proposed Action would not increase or decrease aircraft operations<br />

as compared to the No Action alternative for the same timeframes.<br />

A comparison of the noise contours indicates that the 2014 Proposed Action noise contour would be 0.2 acre<br />

less in size when compared to the 2014 No Action alternative noise contour. As shown in Figure 4-1, the shift<br />

in contour is minor and would result in a minimal decrease in noise exposure. Based on the results of the<br />

noise analysis, there would be no change in population or number of households or other sensitive land uses<br />

exposed to noise levels of CNEL 65 dB or higher when compared to the No Action alternative. Thus, while the<br />

Proposed Action would result in a slight reduction in areas exposed to CNEL 65 dB or higher, no significant<br />

noise impact due to implementation of the Proposed Action would occur.<br />

Table 4-1<br />

Runway Utilization<br />

RUNWAY USE<br />

RUNWAY<br />

Arrivals<br />

Departures<br />

Day Evening Night Day Evening Night<br />

Runway 09 1.36% 1.24% 4.73% .94% 1.13% 0.86%<br />

Runway 27 98.64% 98.76% 95.27% 99.06% 98.87% 99.14%<br />

Total 100% 100% 100% 100% 100% 100%<br />

Source: ANOMS, HMMH<br />

Prepared By: Ricondo & Associates, Inc., March 2013.<br />

<strong>Draft</strong> <strong>EA</strong><br />

Environmental Consequences<br />

[4-3]

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