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Last modified
7/14/2009 5:01:44 PM
Creation date
5/22/2009 4:45:02 PM
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UCREFRP
UCREFRP Catalog Number
7025
Author
Hawkins, J. A. and T. P. Nesler.
Title
Nonnative Fishes in the Upper Colorado River Basin
USFW Year
1991.
USFW - Doc Type
An Issue Paper.
Copyright Material
YES
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<br />18 <br /> <br />Management recommendations <br /> <br />Management recommendations from the literature included suggestions for flow <br />maintenance or regulation, habitat enhancement, preservation of natural habitats and <br />reaches, stocking endangered fish large enough to avoid predation, and protocols for <br />stocking and control of nonnative gamefish. <br /> <br />Several recommendations in the literature warned of altering flow regimes that native <br />fishes coevolved with while other recommendations suggested that flow regimes could be <br />regulated to the advantage of native fishes and a disadvantage of nonnative fishes. Karp and <br />Tyus (1990b) warned that alterations of natural flows in the Yampa River might enhance <br />the further proliferation of nonnative species. They suggested protecting natural flows of <br />the Yampa River. Osmundson (1987) suggested that upstream dams on the Colorado and <br />Gunnison rivers, Colorado, should be discouraged from moderating natural spring flooding <br />that may be useful in controlling nonnative fishes. <br /> <br />Osmundson and Kaeding (1989a) suggested that "flows might be controlled to <br />increase temperature and promote spawning earlier in the year" which might improve growth <br />and survival of larval squawfish. High flushing flows during spring may be the only means <br />to control introduced species (Osmundson and Kaeding 1989a; 1991). Osmundson and <br />Kaeding (1991) recommended peak spring flows for the 15-mile (24 kIn) reach of the upper <br />Colorado River, Colorado, that they hoped would decrease introduced fishes. Higher flows <br />were suggested based on the negative relationship between peak flow and nonnative <br />abundance and the positive relationship between peak flow and native abundance. <br />Grabowski and Hiebert 1989) warned that increased water levels might increase shoreline <br />habitat for young native fish, but might also provide habitat for larger predatory introduced <br />fish in backwaters. Valdez (1990) believed that management of flows would only temporarily <br />decrease densities of many nonnatives because of their high reproductive potential. <br /> <br />Minckley and Meffe (1987) suggested that regular flood events might decrease <br />nonnatives and allow natives a chance to recover from predation or competition, allowing <br />the two faunas to coexist Regular floods would shift the advantage to native fishes that <br />could probably survive this type of event better than most nonnatives. Although they were <br />directing this action toward small streams the applicability for larger rivers and spring run-off <br />flooding remains to be shown. Several predatory centrarchids and ictalurids have been <br />reduced or eliminated by flooding in Arizona streams while natives were little affected <br />However some extreme flood events may decrease or even decimate native populations and <br />drastically alter habitat by bank cutting (Meffe 1984). <br /> <br />Habitat enhancement has was also recommended as a method to enhance native fish <br />populations, but any habitat modification must account for the affects on nonnative fishes. <br />Behnke (1980) suggested the creation of backwaters for mitigation of development. The <br />backwaters would serve as nursery grounds of rare fishes and control structures could be <br />installed to exclude nonnative predators and competitors. Johnson (1980) warned that these <br />
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