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STOCKING PLAN FOR RAZORBACK SUCKER <br />IN THE UPPER COLORADO AND GUNNISON RIVERS <br />I. INTRODUCTION <br />The razorback sucker (Xyrauchen texanus) is one of several native fishes <br />that were formerly common and widespread throughout warm-water reaches of the <br />Colorado River Basin, primarily in the mainstem and large tributaries from <br />Wyoming to Mexico. Razorback sucker numbers have declined appreciably since <br />human alteration of the aquatic environment began in the basin near the turn <br />of this century. The decline of the razorback sucker is attributed to changes <br />in physical and biotic factors leading to very low recruitment because of high <br />mortality during the larval and juvenile life stages. Because of its <br />precarious position, the U. S. Fish and Wildlife Service (USFWS) listed the <br />razorback sucker as an endangered species (effective 22 November 1991; Federal <br />Register, Vol. 56, No. 205, 23 October 1991) under authority of the Endangered <br />Species Act of 1973 (USFWS 1973). <br />This stocking plan provides the rationale to re-introduce razorback sucker <br />in both the Upper Colorado River (Rifle, Colorado downstream to its confluence <br />with the Green River: river miles 241-0) and Gunnison River (river miles 68- <br />0.7) with the intent of re-establishing a population between 1995 and 2000. <br />The short-term goal of this initial stocking effort is to establish an adult <br />population of 10 adults per river mile in floodplain reaches of the two <br />rivers. The long range or ultimate goal is to establish self-sustaining <br />populations in both the Colorado and Gunnison rivers. The target number does <br />not include fish that may occupy off-channel habitats (e.g., gravel-pit <br />ponds). <br />The target for a razorback sucker population in the Upper Colorado and <br />Gunnison rivers will be modified when the Biology Committee's Interim <br />Management Objectives (IMOs) are developed. The IMOs will provide some <br />biological parameters that describe a self-sustaining razorback sucker <br />population. The stocking plan will be reviewed periodically by the Biology <br />Committee. It will be revised as necessary, based on IMOs and results of the <br />proposed stocking and monitoring experiments. <br />II. BACKGROUND <br />Most investigators (e.g., Tyus 1987 et al.; Osmundson and Kaeding 1989; <br />Bestgen 1990) consider the razorback sucker to be much more rare than the <br />Colorado squawfish (Ptychocheilus lucius). Total numbers of razorback sucker <br />collected from the Upper Colorado River have declined dramatically since 1976. <br />Fifty-two razorback sucker were collected during 1976-1981 from Lake Powell to <br />Rifle, Colorado; 35 razorback sucker were captured during 1982-1985; and seven <br />fish were collected from 1986-1989 (Burdick 1992). The last adult razorback <br />sucker in the Gunnison River was captured in 1981 (Holden et al. 1981). Since <br />1988, only ten adult razorback sucker have been captured from riverine <br />environments in the Upper Colorado River-three in 1988, three in 1992, three <br />in 1993, and one in 1995. About 125 adult razorback sucker have been <br />collected recently from lentic habitats in man-made gravel-pit ponds. The