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_ 4 0-Ty k5 <br />North American Journal of Fisheries Management 9:68-73, 1989 <br />Population Size and Status of the Razorback Sucker in the <br />Green River Basin, Utah and Colorado <br />STEVEN H. LANIGAN' AND HAROLD M. TYUS <br />U.S. Fish and Wildlife Service, 1680 West Highway 40, Room 1210 <br />Vernal, Utah 84078, USA <br />Abstract.-The status of the razorback sucker Xyrauchen texanus in the Green River, Utah, was <br />evaluated with capture-recapture data collected from 1980 to 1988. The razorback sucker popu- <br />lation in the upper Green River (river kilometers 282-555) was estimated at 948 fish (95% con- <br />fidence interval, 758-1,138), based on a total of 410 fish captured (68 recaptured). Razorback <br />suckers in the lower Green River (km 0-211) were extremely rare; their numbers were too small <br />(13 fish captured, 1 recaptured) to allow a reliable population estimate. Gray and lower Desolation <br />canyons separated the upper and lower Green River razorback sucker populations. These canyons <br />and a low diversion dam appeared to be barriers to fish movement. The absence of the razorback <br />sucker in Gray and lower Desolation canyons (km 211-282) suggested a lack of suitable habitat. <br />The Green River supports the largest known population of razorback suckers among the species' <br />native riverine habitats. However, low population density and recruitment, as well as habitat <br />alteration, mandate increased research and management efforts to save this population. <br />The razorback sucker Xyrauchen texanus is en- <br />demic to the Colorado River basin of western North <br />America (Minckley 1983). This species, once <br />abundant and widely distributed (Seethaler et al. <br />1979), is now threatened with extinction (McAda <br />and Wydoski 1980; Wick et al. 198; Tyus 1987; <br />USFWS 1987). In riverine habitats, it exists only <br />in the mainstream and lower parts of tributaries <br />of the Green and upper Colorado rivers (McAda <br />and Wydoski 1980; Tyus et al. 1982; Tyus 1987). <br />Razorback sucker populations remain in main- <br />stream reservoirs in the lower Colorado River ba- <br />sin below Lee Ferry, Arizona (Carlson and Carlson <br />1982), but these are relict subpopulations of very <br />old individuals (Minckley 1983; McCarthy and <br />Minckley 1987). <br />The precarious existence of the razorback sucker <br />in the upper Colorado River basin was noted by <br />McAda and Wydoski (1980), Wick et al. (1982), <br />and Tyus (1987), but no attempt at estimating the <br />population size has been published. We evaluated <br />the status of this rare species in the Green River, <br />Utah and Colorado, using capture-recapture data <br />collected from 1980 to 1988. <br />Methods <br />Personnel of the U.S. Fish and Wildlife Service, <br />Colorado River Fish Project (USFWS) and the <br />Utah Division of Wildlife Resources (UDWR) <br />collected razorback suckers in the Green River <br />Present address: Nez Perce National Forest, Route <br />2, Box 475, Grangeville, Idaho 83530, USA. <br />Basin (Figure 1) primarily by electrofishing; a few <br />fish were also collected in seine and trammel nets. <br />The upper and lower boundaries for sampling were <br />river kilometers 35-555 in the Green River (mea- <br />sured from the river mouth), km 0-169 of the <br />Yampa River, and km 0-235 of the White River. <br />Data from two USFWS electrofishing sampling <br />programs were used: data collected during April- <br />June 1980-1981 as part of a basinwide "stan- <br />dardized" program (Tyus et al. 1982) and data <br />from a "spring" program conducted during April- <br />June 1984-1988 (Tyus 1987). Sampling by UDWR <br />personnel was done during April and May of 1986, <br />1987, and 1988, as part of a spring monitoring <br />program for Colorado squawfish Ptychocheilus lu- <br />cius. This program encompassed km 539-483, <br />418-394, and 185-154 of the Green River and km <br />34-0 and 153-167 of the White River. Although <br />all reaches of the rivers described in this paper <br />were sampled, effort varied among reaches be- <br />cause of varying habitat, remoteness, logistics, and <br />sampling goals among the years and programs. <br />Sampling effort was reduced in areas (e.g., White <br />and upper Yampa rivers) where no razorback <br />suckers were found during the systemwide stan- <br />dardized program of 1980-1981. Additional spring <br />electrofishing was conducted in suspected razor- <br />back sucker habitats during 1980-1988. <br />Yearly capture-recapture data for razorback <br />suckers for 1980-1987 were entered as a data ma- <br />trix into the computer program CAPTURE (White <br />et al. 1982). This program tests capture probability <br />assumptions by comparing the absolute and rel- <br />ative fits of eight population estimation models to <br />68 <br />07