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Last modified
8/11/2009 11:32:58 AM
Creation date
8/10/2009 5:14:05 PM
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UCREFRP
UCREFRP Catalog Number
9711
Author
Coggins, L.G.
Title
Abundance trends and status of the Little Colorado River population of humpback chub
USFW Year
2008.
USFW - Doc Type
an update considering 1989-2006 data.
Copyright Material
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<br />Abundance Trends and Status of the Little Colorado River <br />Population of Humpback Chub: An Update Considering <br />1989-2006 Data <br /> <br />By Lewis G. Coggins, Jr. <br /> <br />Executive Summary <br /> <br />In 1967, the humpback chub (Gila cypha) (HBC) was <br />added to the federal list of endangered species and is today <br />protected under the Endangered Species Act of 1973. Only six <br />populations of humpback chub are currently known to exist, <br />five in the Colorado River Basin above Lees Ferry, Arizona, <br />and one in Grand Canyon, Arizona. The majority of Grand <br />Canyon humpback chub are found in the Little Colorado <br />River (LCR)-the largest tributary to the Colorado River in <br />Grand Canyon-and the Colorado River near its confluence <br />with the Little Colorado River. Monitoring and research of the <br />Grand Canyon humpback chub population is overseen by the <br />U.S. Geological Survey's (USGS) Grand Cmyon Monitoring <br />and Research Center (GCMRC) under the auspices of the Glen <br />Canyon Dam Adaptive Management Program (GCDAMP), a <br />Federal initiative to protect and improve resources downstream <br />of Glen Canyon Dam. <br />This report provides updated information on the status <br />and trends of the LCR population in light of new information <br />and refined assessment methodology. An earlier assessment <br />of the LCR population (Coggins and others, 2006a) used data <br />collected dming 1989-2002; the assessment provided here <br />includes that data and additional data collected through 2006. <br />Catch-rate indices, closed population mark-recapture model <br />abundance estimates, results from the Oliginal age-stmctured <br />mark recapture (ASMR) model (Coggins and others, 2006b), <br />and a newly refined ASMR model are presented. This report <br />also seeks to (I) formally evaluate alternative stock assess- <br />ment models using Pearson residual analyses and information <br />theoretic procedures, (2) use mark-recapture data to estimate <br />the relationship between HBC age and length, (3) translate <br />uncertainty in the assignment of individual fish age to result- <br />ing estimates of recmitment and abundance from the ASMR <br />model, and (4) evaluate past and present stock assessments <br />considering the available data sources and analyses, recogniz- <br />ing the limitations inherent in both. <br />A major task of this study was to improve the overall <br />methodology used to conduct HBC stock assessment by <br />addressing concems identified in an independent review <br />conducted in 2003 (Kitchell and others, 2003). The review <br /> <br />report identified that the current technique of assigning age <br />to individual tish based on length was a potential source of <br />bias in ASMR estimates of abundance and recruitment, and <br />called for a more complete examination of this potential error <br />source. Additionally, the review suggested that further work <br />to develop procedures to better arbitrate among alternative <br />assessment models (e.g., ASMR 1-3) would be beneficial. <br />To address the tirst of the concerns identified by the <br />independent review, this study uses mark-recapture data to <br />develop a temperature-dependent growth model to character- <br />ize the relationship between HBC age and length. This model <br />attempts to account for temperature diHerences resulting from <br />both ontogenetic habitat shifts between the Little Colorado and <br />the mainstem Colorado Rivers as well as seasonal variation <br />in water temperature within the LCR. The resulting growth <br />model is then used to characterize the enol' in assigning age to <br />individual fish based on length. Results presented in this study <br />suggest that ageing error does not result in large bias in either <br />abundance or recruitment estimates from the ASMR model. <br />However, incorporating ageing error into the assessment does <br />result in less precise estimates, particularly for recruitment. <br />To address the second concern brought forward in the <br />review repOlt related to model selection procedures, this study <br />arbitrated among the competing models by both examining <br />model fit using Pearson residual analyses and considering <br />information theoretic measures. Although adult abundance <br />estimates and trend varied little among all models considered, <br />these procedures identitied ASMR 3 as the model whose <br />underlying assumptions were most consistent with the data. <br />Because ASMR 3 is also the most complex model. with a <br />structure that allows for complex patterns in capture probabil- <br />ity across ages and through time, further examination of model <br />results suggest a decline in sampling efficacy for middle- <br />aged fish since approximately 2001. Although the cause of <br />this shift in sampling efficacy is still unknown, it is possible <br />that changes in the timing of LCR sampling events or subtle <br />changes in sampling gear may be, at least, partly responsible <br />for this tindi ng. <br />MonitOling data and assessment model results reported <br />herein continue to support the hypothesis that the adult <br />(age-4+) component of the LCR population experienced <br />
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