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NMFS Biological Opinion on U.S. Navy training ... - Govsupport.us

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FINAL PROGRAMMATIC BIOLOGICAL OPINION ON U.S. NAVY ACTIVITIES IN THE HAWAII RANGE COMPLEX 2008-2013<br />

3. underwater det<strong>on</strong>ati<strong>on</strong>s associated with an exercise;<br />

4. aircraft operati<strong>on</strong>s that occur during an exercise,<br />

5. amphibio<strong>us</strong> landings, and<br />

6. gunfire and missile exercises.<br />

Our secti<strong>on</strong> 7 c<strong>on</strong>sultati<strong>on</strong> c<strong>on</strong>sidered the number of endangered or threatened marine animals (that is, those marine<br />

animals that are under the jurisdicti<strong>on</strong> of the Nati<strong>on</strong>al Marine Fisheries Service) that might be exposed to these<br />

different stressors, the nature of those exposures, the animal’s probable resp<strong>on</strong>ses up<strong>on</strong> being exposed, and the risks<br />

those resp<strong>on</strong>ses might pose to individual animals, the populati<strong>on</strong>s those individuals represent, and the species those<br />

populati<strong>on</strong>s comprise.<br />

2.2.1 Exposure Analyses<br />

As disc<strong>us</strong>sed in the introducti<strong>on</strong> to this secti<strong>on</strong> of this <str<strong>on</strong>g>Opini<strong>on</strong></str<strong>on</strong>g>, exposure analyses are designed to identify the listed<br />

resources that are likely to co-occur with these effects in space and time and the nature of that co-occurrence. Our<br />

exposure analyses are designed to identify the number, age (or life stage), and gender of the individuals that are<br />

likely to be exposed to an Acti<strong>on</strong>’s effects and the populati<strong>on</strong>s or subpopulati<strong>on</strong>s those individuals represent.<br />

Exposure to <strong>Navy</strong> Vessel Traffic<br />

To estimate the number of endangered or threatened species that are likely to be exposed to vessel traffic associated<br />

with those U.S. <strong>Navy</strong> <strong>training</strong> and other activities in the Hawai'i Range Complex, we began with encounter rates<br />

(that is, n/L, or the number of marine mammal groups per unit distance or, in our case, groups per nautical mile)<br />

reported by vario<strong>us</strong> investigators in the Hawai'ian Islands (for example, Baird et al. 2003, Baird 2005, Mobley 2001,<br />

2004, 2006, 2008; Norris et al. 2005, Smultea et al. 2008). When data were available, we <strong>us</strong>ed encounter rates that<br />

reflected seas<strong>on</strong>al and geographic differences, then multiplied encounter rates by the number of hours vessels<br />

participating in a <strong>training</strong> activity might travel multiplied by nominal travel speeds of 10 knots ( = nominal number<br />

of vessels • vessel speed • hours of travel). Finally, we multiplied the resulting number of encounters by the mean<br />

group size for the different species to estimate the number of individuals that might be exposed to vessel traffic. That<br />

is<br />

No. individuals exposed to vessel traffic = (Encounter rate • Hours of transit) • mean group size<br />

where encounter rate might represent the number of groups encountered per unit distance (<strong>us</strong>ing nautical miles as the<br />

reference point) or unit time (hours).<br />

Exposure to Active S<strong>on</strong>ar<br />

Despite the numero<strong>us</strong> surveys that have been c<strong>on</strong>ducted in the Hawai'ian Islands and reports from whale-watch<br />

vessels in the Hawai'ian Islands, there is almost no empirical informati<strong>on</strong> <strong>on</strong> the distributi<strong>on</strong> and abundance of<br />

marine mammals relative to active s<strong>on</strong>ar associated with <strong>Navy</strong> <strong>training</strong> exercises. We do not know whether or to<br />

what degree the distributi<strong>on</strong> or abundance of marine animals changes before, during, or after an exercise or whether<br />

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