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Last modified
8/11/2009 11:32:58 AM
Creation date
8/10/2009 5:03:59 PM
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Template:
UCREFRP
UCREFRP Catalog Number
9549
Author
Bestgen, K. R., K. A. Zelasko, R. I. Compton and T. Chart.
Title
Response of the Green River Fish Community to Changes in Flow Temperature Regimes from Flaming Gorge Dam since 1996 based on sampling conducted from 2002 to 2004.
USFW Year
2006.
USFW - Doc Type
115,
Copyright Material
NO
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A main challenge of testing river restoration hypotheses is linking population <br />measurements such as fish abundance to a driving variable or set of variables with reasonable <br />certainty. For example, it is difficult to isolate effects of flow or temperature regimes when <br />distribution and abundance of invasive species are expanding, perhaps though interactions with <br />variable environmental conditions (Bestgen et al. In press). Because cause and effect <br />experiments are not possible in this setting, correlations and weight of evidence approaches are <br />the prevailing technique to accomplish this (Beyers 1998). Populations that are composed of <br />species whose biology is poorly understood and which are relatively long-lived make these <br />assessments more difficult, because responses to changes are slow and assignment of causative <br />factors is difficult. <br />The reach of the Green River, Utah and Colorado, downstream of Flaming Gorge Dam <br />offers an opportunity to evaluate effectiveness of actions to re-establish native fishes. This is an <br />ideal study area because more natural hydrologic and temperature regimes designed to benefit <br />native fishes have been implemented over a series of years. The Green River also has a source <br />pool of native fishes downstream, including the mostly unregulated and tributary Yampa River <br />and regulation-attenuated downstream reaches of the Green River, to re-colonize upstream <br />reaches. Furthermore, descriptions of the fish community are available from immediate pre-dam <br />(pre-1962) and post-dam (1964-1966) periods, as well as before and after installation of a <br />temperature control device (1978-1980). Additional sampling was conducted from 1994 to 1996 <br />that further evaluated changes in the fish community following implementation of flow <br />recommendations contained in the 1992 Biological Opinion on operation of Flaming Gorge Dam <br />(U. S. Fish and Wildlife Service 1992, Bestgen and Crist 2000). <br />Since 1996, a new set of flow and temperature recommendations for the Green River was <br />developed (Muth et al. 2000). Those recommendations will not be fully implemented until <br />Endangered Species Act and National Environmental Policy Act compliance activities are <br />complete, which is expected in 2006. Annual peak and base flow recommendations were <br />developed for each of five hydrologic conditions that ranged from dry to wet, based on <br />exceedance probabilities: dry (90 to 100% exceedance), moderately dry (70 to 90% exceedance), <br />2
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