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Last modified
7/14/2009 5:02:36 PM
Creation date
5/22/2009 6:50:38 PM
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UCREFRP
UCREFRP Catalog Number
9576
Author
Utah Department of Natural Resources.
Title
Conservation and Management Plan for Three Fish Species in Utah - Adressing needs for Roundtail Chub (Gila robusta), Bluehead Sucker (Catostomus discobolus), and Flannelmouth Sucker (Catostomus latipinnis).
USFW Year
2006.
USFW - Doc Type
Salt Lake City, UT.
Copyright Material
NO
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<br />Executive Summary <br />Page 5 <br />~ This plan is an effort to prevent the listing of three fish species (roundtail chub, bluehead sucker, <br />and flannelmouth sucker) through proactive conservation of their populations and habitat <br />throughout the state of Utah. Each of these species has experienced population declines in recent <br />years due to habitat loss through water development, the introduction of nonnative species as <br />both predators and competitors, and indirect effects brought about by these impacts. This <br />~ observed decline in population numbers suggests these three species are in a situation that <br />warrants their conservation. Because these species are not sportfish or listed species, they have <br />historically received limited attention by wildlife management agencies. Preventing the listing of <br />these species through proactive conservation is expected to benefit the Utah Division of Wildlife <br />Resources (Division), other natural resource managers, and the communities surrounding three <br />~ species habitats. <br />This is a cooperative effort between a number of land and water resource agencies around the <br />state. Each cooperator has a specific management authority that not only allows their <br />participation in this effort, but also makes them essential to this process. Funding has been <br />provided for development of this plan and the collection of baseline information through the <br />State's Endangered Species Mitigation Fund and the Fish and Wildlife Service's (Service) State <br />Wildlife Grants. This funding has been essential in completing tasks to this point and will be <br />pursued in future years as we implement identified conservation actions. <br />The current environment of these species is quite different from that of 100 years ago when all <br />~ three species were considered common to all of their historical localities in the Colorado River <br />Basin (Bezzerides and Bestgen 2002). Water development and diversion began with the <br />Reclamation Act of 1902 and has progressed such that some systems in the state are highly <br />artificial and others are at least highly impacted by varying types of surface water diversions. <br />Especially in drought years, these diversions contribute to seasonal de-watering of entire <br />~ stretches of stream after run-off flows have subsided. In addition to very different flow regimes, <br />the community assemblage is quite different today than it was 150 years ago, after which time <br />wildlife agencies began to stock nonnative fish species for human consumption and a source of <br />angler recreation. In fact, only 14 species are considered native and over 60 species have been <br />introduced (intentionally or accidentally) in the upper basin (Minckley 1991, Martinez et al. <br />~ 1994, Valdez and Carothers 1998). These native fishes evolved to be specifically adapted to a <br />very demanding and harsh environment. The human development of this environment reduced <br />the variability of flows in the upper basin, which coupled with the introduction of competitors <br />and previously unknown predators into the system, was detrimental to native species. Bezzerides <br />and Bestgen (2002), the only range-wide status review for all three species suggests that impacts <br />. have been more severe for roundtail chub and bluehead sucker. <br />In order to adequately address these impacts, we have developed an approach that requires the <br />identification of the exhaustive list of potential projects and annual prioritization of these <br />projects based on the amount of information known in each hydrologic unit of interest, the risks <br />posed to the three species within the hydrologic unit, and the opportunities present in each <br />~ hydrologic unit. Initially, many of these prioritization steps will lead us to continue to fill in <br />information gaps and implement actions to prevent losses of known populations. In time, when <br /> <br />
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