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Last modified
7/14/2009 5:02:30 PM
Creation date
5/22/2009 7:24:38 PM
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UCREFRP
UCREFRP Catalog Number
7713
Author
U.S. Fish and Wildlife Service, C. R. F. R. T.
Title
Colorado Squawfish Recovery Plan.
USFW Year
1991.
USFW - Doc Type
\
Copyright Material
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1 <br /> In September 1962, the area of the Green River now impounded by Flaming Gorge <br /> Dam was treated with rotenone in order to establish more favorable conditions <br /> for game fish species. This poisoning effectively eliminated Colorado <br /> squawfish in the reservoir basin, and an accident occurred in which a small <br /> proportion of the toxic substance apparently travelled downstream past a <br /> detoxification station to the vicinity of Dinosaur National Monument. Banks <br /> (1964) noted a significant reduction in the number of species captured at four <br />' stations within Dinosaur National Monument shortly after the accidental <br /> treatment. The greatest reduction appeared to occur at the Gates of Lodore in <br /> the northern and most upstream portion of Dinosaur National Monument, while <br /> the least impact was noted at a downstream site. However, Binns et al. (1963) <br /> concluded that little long-term impact to the fish species composition had <br /> resulted from the treatment. <br />' Colorado squawfish have disappeared from areas upstream of reservoirs (e.g., <br /> Salt River above Roosevelt Lake, Arizona; Green River above Fontenelle and <br /> Flaming Gorge dams, Wyoming; San Juan River above Navajo Reservoir, New <br />1 Mexico) and in reaches that appear little changed from predevelopment <br />ll <br /> y <br />conditions. Reasons for these disappearances or declines are not fu <br /> understood, but probably involve subtle changes in habitat, competition and <br /> predation from introduced species, blockage of spawning migrations, lack of <br /> suitable spawning habitat, post-dam eradication programs, and/or loss of adult <br /> fish from angling. In summary, the absolute cause for the decline of Colorado <br /> squawfish is not fully understood but is probably related to a combination of <br /> factors, including direct loss of habitat, changes in flow and temperature, <br /> blockage of migration routes, and interactions with introduced fish species. <br />' Sensitive Areas and Priority Recovery Areas <br /> Sensitive Areas <br />' The Biological Subcommittee of the Upper Colorado River Coordinating Committee <br /> developed criteria and prepared a list of sensitive areas depicting the <br /> location of important spawning, nursery, juvenile, and- adult habitats, both <br />' past and present, in the Upper Basin (U.S. Fish and Wildlife Service 1987) <br /> (Figure 3). The Recovery Team has adopted this report and has recommended <br /> that a similar document based on appropriate criteria be developed for the <br />' Lower Basin. Because Colorado squawfish have been extirpated from the Lower <br /> Basin, criteria would be established primarily to identify priority areas for <br /> research and recovery. <br />' Priority Areas for Recovery <br /> The highest priority Colorado squawfish recovery areas occur in the Upper <br />' Basin, and include, in order of importance, the Green, Colorado, and San Juan <br /> subbasins. The Green River subbasin includes the mainstem Green, Yampa, <br /> Little Snake, White, and Duchesne Rivers. The Colorado River subbasin <br /> includes the Gunnison and the Dolores Rivers, and the San Juan subbasin <br /> includes the Animas River. The Green River subbasin contains the largest and <br /> most viable population of squawfish in the Colorado River basin (Tyus 1991b). <br /> As such, the Green River and its tributaries constitute the highest priority <br /> site for recovery and maintenance of Colorado squawfish. <br />17 <br />
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