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<br />based on available data and proposed values were presented to describe an <br />"improving condition" desired for each parameter for each population. Species' <br />distribution, population estimates, density, recruitment rate,. survival rate, and age <br />composition were estimated using data available through 1991. Since then, the <br />Recovery Program implemented a fish tagging effort using Passive Integrated <br />Transponder (PIT) tags to mark all endangered fish captured or stocked. <br />Compared to the previous use of externally-fastened Carlin tags, loss of PIT tags <br />from marked fish is negligible, and enhances our ability to identify individual fish in <br />the population, increase the number of marked fish in the population, and estimate <br />population size. In the eight years since the Colorado IROs were developed, new <br />information based on these PIT tags is available to update and refine certain <br />population parameters, including population size and recruitment. Other studies <br />within the Recovery Program provide information such as adult survival rates for <br />Colorado pikeminnow and point estimates of population size for select species in <br />select river reaches for comparison. On the other hand, age data and survival <br />estimates based on age composition of individual populations have not been <br />updated since 1992. The premise of this approach is that the fish data available <br />from standardized monitoring and population estimation sampling is sufficient to <br />develop measurable criteria for downlisting and delisting goals. <br /> <br />The stated purpose of the Endangered Species Act (ESA) is "to provide a <br />means whereby the ecosystems upon which endangered species and threatened <br />species depend may be conserved" (ESA 16 U.S.C. 1531). This purpose does not <br />imply that the species must be restored fully to its historic range. The definition of <br />"conserve" within ESA is "to use and the use of all methods and procedures which <br />are necessary to bring an endangered species or threatened species to the point <br />at which the measures provided pursuant to this chapter are no longer necessary <br />(ESA 16 U.S.C. 1532). It is important to note that "recovery" is not defined within <br />ESA, but could be interpreted to be the "poinf' referred to in the definition of <br />conservation. Recovery is a species-specific attribute bounded by the definition of <br />"conservation" within ESA. Recovery may be defined as restoration of a target <br />species demographic status and trend to a condition where it is no longer in <br />danger (threatened or endangered) of becoming extinct. Restoration of the <br />species to greater levels of distribution and abundance within its historic range <br />(beyond recovery from a decline toward extinction and within a secure, supporting' <br />ecosystem) is not the intended purpose of ESA. The approach used here focuses <br />on inclusion of populations and their habitat where a potential for persistence is <br />feasible based on existing biological data. <br /> <br />The over-ridinQ criterion associated with recovery is that recruitment <br />to adult populations is Qenerated throuQh natural reproduction in the wild. <br />Additional definitions of recovery for these fishes can be reduced to key population <br />parameters, or criteria, including number of populations, distribution, abundance, <br />recruitment to the adult population, and population size structure. All of these <br />parameters can be determined or estimated annually from field data using <br />consistent methodology. The goals established for each of the listed fish species <br /> <br />2 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br /> <br />'. <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />