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Last modified
7/14/2009 5:02:35 PM
Creation date
5/22/2009 4:53:39 PM
Metadata
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UCREFRP
UCREFRP Catalog Number
9378
Author
Nesler, T. P.
Title
Recovery of the Colorado River Endangered Fishes
USFW Year
2000.
USFW - Doc Type
Biological recovery goals and criteria for Colorado pikeminnow, Humpback chub, Razorback sucker & Bonytail.
Copyright Material
NO
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<br />6 <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 />I <br />I <br />I <br />I <br />I <br />I <br /> <br />sexual maturity necessary to be part of the adult population. It is assumed that <br />these fish are completely vulnerable to capture by net and electrofishing sampling. <br />The percent of this size group to the total number of fish used in the distribution <br />represented annual recruitment, and was estimated for each year a length <br />frequency distribution could be constructed. This approach is an indirect means of <br />characterizing and maintaining stability in the population in terms of successful <br />reproduction of young and survival to the adult stage. <br /> <br />Length frequency distributions were condensed into three major size <br />categories to characterize the size structure of the population. These size groups <br />included a small-size category for fish less than recruitment size, a mid-size <br />category for the bulk of the adult population, and a large-size category for the older <br />adults. The purpose for designating these categories was to describe and <br />maintain the observed size structure of the population. This use of length <br />frequency categories was also an indirect means of maintaining stability in the <br />adult population in terms of age composition, growth and survival. A percentage <br />range was provided for each size category for each population using rolling <br />averages of annual estimates as a means of accounting for natural variability <br />between populations and smoothing year-to-year variability in reproduction, year <br />class strength, and mortality/survival within populations. These rolling averages <br />were based on the observed annual length frequency distributions. Where the <br />number of annual estimates permitted, rolling five-year averages for Colorado <br />pikeminnow and three-year averages for humpback chub were examined for each <br />size group. The use of five and three-year rolling averages for Colorado <br />pikeminnow and humpback chub, respectively, was part arbitrary and part a <br />reflection of differences in maturation ages between the two species. The annual <br />variation observed is likely a result of a combination of natural and sampling <br />variability. The recruitment criteria are also presented as rolling averages to offset <br />the impact of annual variation and provide a more coherent criterion. <br /> <br />Other Criteria: Along with measurable biological criteria, one of the <br />benchmarks of recovery is demonstration of adequate habitat protection. For <br />these fish species, the primary habitat concerns are flows, flow regime, flooded <br />bottomland/backwater nursery habitats, instream passage and non-native fish <br />populations. Given uncertainty in what is needed in these habitat areas to achieve. <br />and maintain biological recovery goals, institutional agreements controlling <br />nonnative fishes stocking, flow maintenance and other habitat management <br />provide a means for developing protective measures for perceived and existing <br />threats without implicating downlisting requirements, statutes, or regulation for <br />experimental measures. Recovery goals should be sufficient to sustain <br />populations in the face of threats that will continue to exist if they cannot be <br />removed or reasonably reduced. Evaluation of population parameters in existing <br />populations that appear stable or improving under existing environmental variables <br />and threats is a logical basis for determining recovery goals for these fish species. <br />If populations of the listed fish species are documented as meeting the biological <br />goals necessary for delisting, then it is reasonable to assume that the necessary <br />
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