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14 <br />razorback sucker hybrids in the present collection does <br />not necessarily indicate fewer hybrids in the system, <br />but may be due to variations in sampling locations or <br />other factors. Misidentification of younger hybrids is <br />possible because of their close resemblance to the <br />flannelmouth sucker. However, large hybrids are <br />readily identifiable by their small dorsal ridge and <br />intermediate lip structure. <br />Future of the Razorback Sucker in the <br />Colorado River Basin <br />The Yampa River plays a major role in the continued <br />survival of the razorback sucker and other native <br />fishes. The Green River begins to resume its natural <br />temperature regime as it gains warmer water from the <br />Yampa River. The ameliorating impact of the Yampa <br />River on the Green River is believed to be important to <br />the razorback sucker and the other native fish in the <br />river system (Holden and Stalnaker 1975b~. Vanicek et <br />al. (1970) documented the reduction in native fish <br />populations of the Green River above the mouth of the <br />Yampa River after the closure of Flaming Gorge <br />Reservoir. The four rare native fish (Colorado squaw- <br />fish, razorback sucker, humpback chub, and bonytail <br />chub) were eliminated from the Green River above the <br />confluence with the Yampa at that time. Their decline <br />was associated with alterations in temperature, <br />streamflow, turbidity, and other characteristics of the <br />river. The Yampa River partly restored the historical <br />water conditions in the Green River, sufficiently to <br />allow the fish to survive below the confluence of the <br />two rivers. <br />The Yampa River is the largest free-flowing river <br />that remains in the Colorado River basin. In this <br />basin, about one-fourth (22%) of the river length is <br />inundated by reservoirs (Utah Water Research <br />Laboratory 1975) and most of the remaining reaches <br />have been adversely affected by water releases from <br />these reservoirs. Alterations to the natural tem- <br />perature regime of the Yampa River could be detri- <br />mental to the native fauna, particularly to the four <br />threatened or endangered fishes. The Green River, <br />from the confluence with the Yampa River to its <br />mouth in Canyonlands National Park, contains most <br />of the remaining large-river habitat in the Colorado <br />basin. Any changes in water temperature or stream- <br />flow that occur upstream, such as the Yampa River, <br />could significantly reduce the remaining habitat of <br />these four species. <br />The decline of the razorback sucker is well correlated <br />with the development of the Colorado River basin. <br />However, the specific changes that have caused the <br />decline are not yet clear. Sections of the Green and <br />Yampa rivers are relatively unaltered, but contain <br />only small numbers of razorback suckers, whereas <br />other native species are still abundant. Reproductive <br />failure appears to be a major factor in the decline of the <br />species. However, the reason for this failure is difficult <br />to determine because a closely related fish-the <br />flannelmouth sucker-which appears to have similar <br />spawning requirements (McAda 1977, is still doing <br />well. <br />Acknowledgments <br />We thank G. Kidd, formerly of the Colorado Divi- <br />sion of Wildlife, who participated in several collec- <br />tions; K. Seethaler, D. Cox, J. Henderson, L. Maclain, <br />and C. Reger, who assisted in the field; J. King, C. <br />Larson, K. Priest, K. Rudd, and J. Wydoski, who <br />helped with the laboratory work. <br />References <br />Bagenal, T. B. 1967. A short review of fish fecundity. Pages <br />89-111 in S. D. Gerking, ed. The biological basis of fresh- <br />water fish production. Blackwell Sci. Publ., Oxford. <br />Banks, J. L. 1964. Fish species distribution in Dinosaur Na- <br />tional Monument during 1961-1962. M. S. Thesis. Colorado <br />State University, Fort Collins. 96 pp. <br />Chamberlain, F. M. 1904. Notes on fishes collected in Ari- <br />zona. 1904. U. S. National Museum, Washington, D. C. <br />56 pp. (Unpubl. rep.) <br />Constantz, G. D. 1974. Values of endangered fishes for study <br />of basic biological concepts: the Gila topminnow, Poecili- <br />opsis occidentalis, as an example. Proc. Annu. Conf. West. <br />Assoc. State Game Fish Comm. 54:280-285. <br />Deacon, J. E. 1968. Endangered non-game fishes of the West; <br />causes, prospects, and importance. Proc. Annu. Conf. <br />West. Assoc. State Game Fish Comm. 48:534-549. <br />Dill, W. A. 1944: The fishery of the lower Colorado River. <br />Calif. Fish Game 30~2~:109-211. <br />Dolan, R., A. Howard, and A. Gallenson. 1974. Man's impact <br />on the Colorado River in the ,Grand Canyon. Am. Sci. <br />624):392-401. <br />Douglas, P. A.1952. Notes on the spawning of the humpback <br />sucker, Xyrauchen texanus (Abbott-. Calif. Fish Game <br />38~2~:149-155. <br />Everman, B. W. 1916. Fishes of the Salton Sea. Copeia 34:61- <br />63. <br />Geen, G. H. 1974. Effects of hydroelectric development in <br />western Canada on aquatic ecosystems. J. Fish. Res. Board <br />Can. 315-:913-927. <br />Hart, L. G., and R. C. Summerfelt. 1975. Surgical procedures <br />for implanting ultrasonic transmitters into flathead catfish <br />(Pylodictis oliuaris~. Trans. Am. Fish. Soc. 1041-:56-59. <br />Hasler, W. J., E. S. Gardella, R. M. Horrace, and H. F. <br />Henderson. 1969. Open water orientation of white bass, <br />Roccus chrysops, as determined liy ultrasonic tracking <br />methods. J. Fish. Res. Board Can. 268-:2173-2192. <br />Holden, P. B. 1973. Distribution, abundance, and life history <br />of the fishes of the upper Colorado River basin. Ph.D. <br />Thesis. Utah State Univ., Logan. 59 pp. <br />Holden, P. B. 1978. A study of the habitat and movement of <br />the rare fishes in the Green River, Utah. Trans. Bonneville <br />Chapter Am. Fish. Soc. 1:64-89. <br />