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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 />

is, the probability of extincti<strong>on</strong> or probability of persistence) of listed species depends <strong>on</strong> the viability of the<br />

populati<strong>on</strong>s that comprise the species. Similarly, the c<strong>on</strong>tinued existence of populati<strong>on</strong>s are determined by the fate of<br />

the individuals that comprise them; populati<strong>on</strong>s grow or decline as the individuals that comprise the populati<strong>on</strong> live,<br />

die, grow, mature, migrate, and reproduce (or fail to do so).<br />

Our risk analyses reflect these relati<strong>on</strong>ships between listed species and the populati<strong>on</strong>s that comprise them, and the<br />

individuals that comprise those populati<strong>on</strong>s. Our risk analyses begin by identifying the probable risks acti<strong>on</strong>s pose to<br />

listed individuals that are likely to be exposed to an acti<strong>on</strong>’s effects. Our analyses then integrate those individuals<br />

risks to identify c<strong>on</strong>sequences to the populati<strong>on</strong>s those individuals represent. Our analyses c<strong>on</strong>clude by determining<br />

the c<strong>on</strong>sequences of those populati<strong>on</strong>-level risks to the species those populati<strong>on</strong>s comprise.<br />

We measure risks to listed individuals <strong>us</strong>ing the individual’s “fitness,” which are changes in an individual’s growth,<br />

survival, annual reproductive success, or lifetime reproductive success. In particular, we examine the scientific and<br />

commercial data available to determine if an individual’s probable resp<strong>on</strong>se to an Acti<strong>on</strong>’s effects <strong>on</strong> the<br />

envir<strong>on</strong>ment (which we identify in our resp<strong>on</strong>se analyses) are likely to have c<strong>on</strong>sequences for the individual’s<br />

fitness.<br />

When individual, listed plants or animals are expected to experience reducti<strong>on</strong>s in fitness, we would expect those<br />

reducti<strong>on</strong>s to also reduce the abundance, reproducti<strong>on</strong> rates, or growth rates (or increase variance in <strong>on</strong>e or more of<br />

these rates) of the populati<strong>on</strong>s those individuals represent (see Stearns 1992). Reducti<strong>on</strong>s in <strong>on</strong>e or more of these<br />

variables (or <strong>on</strong>e of the variables we derive from them) is a necessary c<strong>on</strong>diti<strong>on</strong> for reducti<strong>on</strong>s in a populati<strong>on</strong>’s<br />

viability, which is itself a necessary c<strong>on</strong>diti<strong>on</strong> for reducti<strong>on</strong>s in a species’ viability. Therefore, when listed plants or<br />

animals exposed to an Acti<strong>on</strong>’s effects are not expected to experience reducti<strong>on</strong>s in fitness, we would not expect that<br />

Acti<strong>on</strong> to have adverse c<strong>on</strong>sequences <strong>on</strong> the viability of the populati<strong>on</strong>s those individuals represent or the species<br />

those populati<strong>on</strong>s comprise (for example, see Anders<strong>on</strong> 2000, Mills and Beatty 1979, Stearns 1992). As a result, if<br />

we c<strong>on</strong>clude that listed plants or animals are not likely to experience reducti<strong>on</strong>s in their fitness, we would c<strong>on</strong>clude<br />

our assessment beca<strong>us</strong>e an Acti<strong>on</strong> that is not likely to affect the fitness of individuals is not likely to jeopardize the<br />

c<strong>on</strong>tinued existence of listed species.<br />

If, however, we c<strong>on</strong>clude that listed plants or animals are likely to experience reducti<strong>on</strong>s in their fitness, our<br />

assessment tries to determine if those fitness reducti<strong>on</strong>s are likely to be sufficient to reduce the viability of the<br />

populati<strong>on</strong>s those individuals represent (measured <strong>us</strong>ing changes in the populati<strong>on</strong>s’ abundance, reproducti<strong>on</strong>,<br />

spatial structure and c<strong>on</strong>nectivity, growth rates, or variance in these measures to make inferences about the<br />

populati<strong>on</strong>’s extincti<strong>on</strong> risks). In this step of our analyses, we <strong>us</strong>e the populati<strong>on</strong>’s base c<strong>on</strong>diti<strong>on</strong> (established in the<br />

Envir<strong>on</strong>mental Baseline and Stat<strong>us</strong> of Listed Resources secti<strong>on</strong>s of this <str<strong>on</strong>g>Opini<strong>on</strong></str<strong>on</strong>g>) as our point of reference. Finally,<br />

our assessment tries to determine if changes in populati<strong>on</strong> viability are likely to be sufficient to reduce the viability<br />

of the species those populati<strong>on</strong>s comprise. In this step of our analyses, we <strong>us</strong>e the species’ stat<strong>us</strong> (established in the<br />

Stat<strong>us</strong> of the Species secti<strong>on</strong> of this <str<strong>on</strong>g>Opini<strong>on</strong></str<strong>on</strong>g>) as our point of reference.<br />

<str<strong>on</strong>g>Biological</str<strong>on</strong>g> opini<strong>on</strong>s, then, distinguish am<strong>on</strong>g different kinds of “significance” (as that term is comm<strong>on</strong>ly <strong>us</strong>ed for<br />

NEPA analyses). First, we foc<strong>us</strong> <strong>on</strong> potential physical, chemical, or biotic stressors that are “significant” in the sense<br />

of “salient” in the sense of being distinct from ambient or background. We then ask if (a) exposing individuals to<br />

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