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the retention of these highly turbid conditions is an important factor for <br />these endangered fishes. Reduction of turbidity may enable introduced species <br />to gain a competitive edge which could further contribute to the decline of <br />the endangered Colorado River fishes. <br />Razorback Sucker <br />The razorback sucker, an endemic species unique to the Colorado River Basin, <br />was historically abundant and widely distributed within warmwater reaches <br />throughout the Colorado River Basin. Historically, razorback suckers were <br />found in the main stem Colorado River and major tributaries in Arizona, <br />California, Colorado, Nevada, New Mexico, Utah, Wyoming, and in Mexico (Ellis <br />1914; Hinckley 1983). Bestgen (1990) reported that this species was once so <br />numerous that it was commonly used as food by early settlers and, further, <br />that commercially marketable quantities were caught in Arizona as recently as <br />1949. In the Upper Basin, razorback suckers were reported in the Green River <br />to be very abundant near Green River, Utah, in the late 1800's (Jordan 1891). <br />An account in Osmundson and Kaeding (1989) reported that residents living <br />along the Colorado River near Clifton, Colorado, observed several thousand <br />razorback suckers during spring runoff in the 1930's and early 1940's. In the <br />San Juan River drainage, Platania and Young (1989) relayed historical accounts <br />of razorback suckers ascending the Animas River to Durango, Colorado, around <br />the turn of the century. <br />A marked decline in populations of razorback suckers can be attributed to <br />construction of dams and reservoirs, introduction of nonnative fishes, and <br />removal of large quantities of water from the Colorado River system. Dams on <br />the main stem Colorado River and its major tributaries have segmented the <br />river system and drastically altered flows, temperatures, and channel <br />geomorphology. Major changes in species composition have occurred due to the <br />introduction of numerous nonnative fishes, many of which have thrived due to <br />man-induced changes to the natural riverine system. <br />The current distribution and abundance of the razorback sucker have been <br />significantly reduced throughout the Colorado River system (McAda 1987; McAda <br />and Wydoski 1980; Holden and Stalnaker 1975; Hinckley 1983; Marsh and Hinckley <br />1989; Tyus 1987). The only substantial population of razorback suckers <br />remaining, made up entirely of old adults (McCarthy and Hinckley 1987), is <br />found in Lake Mohave; however, they do not appear to be successfully <br />recruiting. While limited numbers of razorback suckers persist in other <br />locations in the Lower Colorado River, they are considered rare or incidental <br />and may be continuing to decline. <br />In the Upper Basin, above Glen Canyon Dam, razorback suckers are found in <br />limited numbers in both lentic and lotic environments. The largest population <br />of razorback. suckers in the Upper Basin is found. in the upper Green River and <br />lower Yampa River (Tyus 1987). Lanigan and Tyus (1989) estimated. that from <br />758 to 1,138 razorback suckers inhabit the upper Green River: .In the Colorado . <br />River, most razorback suckers occur in the Grand Valley area near Grand <br />Junction, Colorado; however, they are increasingly rare. Osmundson and <br />Kaeding (1991) report that the number of razorback sucker captures in the <br />Grand Junction area has declined dramatically since 1974.. <br />