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Last modified
7/14/2009 5:02:37 PM
Creation date
5/17/2009 11:21:04 PM
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UCREFRP
UCREFRP Catalog Number
9666
Author
VanHaverbeke, D. R. and Robert L. Simmonds Jr.
Title
Final Report - The Feasibility of Developing a Program To Augment the Population of Humpback Chub (Gila cypha) In Grand Canyon.
USFW Year
2004.
USFW - Doc Type
Flagstaff, AZ.
Copyright Material
NO
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<br />Feasibility of Establishing a Supportive Stocking Program Using Hatchery <br />Produced Fish from a Captive Broodstock <br /> <br />Augmenting wild populations through the release of captive bred individuals is <br />increasingly being used in conservation (World Conservation Union 1987). In 1990, <br />27% of Federal recovery programs in the USA for endangered freshwater fishes <br />included captive breeding as an element of recovery (Andrews and Kaufman 1994), and <br />supportive breeding is a component of the management alternatives for the <br />conservation and recovery of endangered Pacific salmon ids (Hedrick et al. 1994, <br />Waples and Drake 2002). Despite these trends, the merits of hatchery production have <br />been challenged on grounds that supportive breeding often contributes to the problem <br />of threatened or endangered species rather than being a solution (Hilborn 1992, Meffe <br />1992, Lichatowich et al. 1999, Levin et al. 2001, Levin and Williams 2002), and that the <br />majority of such activities have been economic failures (Hilborn 1998, Naylor et al. <br />2000). Waples and Drake (2002) caution that even when managers are aware of all <br />foreseeable risks, the chances are high that unexpected developments will erase <br />projected benefits. Hilborn (1998) states that based upon historical experience, <br />politicians, managers and advocates of new stocking programs should realize that there <br />are limited empirical data that support the long-held belief that supportive stocking has <br />ever been biologically successful. <br /> <br />As a result, managers for threatened or endangered species sometimes face a potential <br />double jeopardy situation. Failure to intervene in a deterministic decline of an <br />endangered species mightresult in extinction. However, using captive broodstock for <br />supplementation may result in changes (primarily genetic) that reduce sustainability and <br />viability of the wild population (Hynes et al. 1981, Allendorf and Ryman 1987, Waples <br />and Do 1994, Levin et al. 2001). <br /> <br />Policy and priority considerations <br /> <br />Within the context of the ESA, the USFWS and the National Oceanic and Atmosphere <br />Administration (NOAA) provide policy guidelines regarding controlled propagation of <br />listed species (U.S. Office of Federal Register 65:183 [2000]: 56916-56922). As defined <br />in the document, controlled propagation includes the production of individuals for <br />"reintroduction to the wild to establish new populations", and to the "holding of offspring <br />for a substantial portion of their development or through a life-stage that experiences <br />poor survival in the wild." <br /> <br />This document explains that "controlled propagation is not a substitute for addressing <br />factors responsible for an endangered or threatened species' decline", and that the "first <br />priority is to recover wild populations in their natural habitat wherever possible, without <br />resorting to the use of controlled propagation." In addition, controlled propagation "will <br />be used as a recovery strategy only when other measures employed to maintain or <br />improve a listed species' status in the wild have failed, are determined to be likely to fail, <br />are shown to be ineffective in overcoming extant factors limiting recovery, or would be <br />insufficient to achieve full recovery." Furthermore, "all reasonable effort should be made <br /> <br />10 <br />
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