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<br />FISHES OF THE COLORADO RIVER IN GRAND CANYON NATIONAL PARKl <br /> <br />Royal D. Suttkus2 and Glenn H. Clemmer3 <br /> <br />The general decline in native fish populations <br />in the American southwest has been documented in <br />numerous studies (Dill 1944; Miller 1946 a,b; <br />Wallis 1951; Minckley and Deacon 1968; Minckley <br />1973 and others). Isolated spring populations <br />and residents of smaller tributaries have been <br />particularly vulnerable to habitat losses and <br />competition with introduced exotic forms. Species <br />inhabiting large rivers have been similarly af- <br />fected; however, their status is more difficult <br />to ascertain. Almost 300 miles of the Colorado <br />River through the Grand Canyon has been virtually <br />inaccessible for ichthyological studies until re- <br />cently. Float trips on large pontoon rafts have <br />opened up the Canyon and have become increasingly <br />popular in the past few years. This increased <br />visitor pressure on the Colorado River and con- <br />comitant attention toward vanishing wildlife re- <br />sources has stimulated our studies on the status <br />of the fishes of the Colorado River in the Grand <br />Canyon National Park. <br /> <br />Our study area extended from Lee's Ferry (which <br />is 15 miles below Glen Canyon Dam) to the upper <br />reaches of the Mead Reservoir at Pierce Landing <br />(River Mile 280). Most of our 13 float trips were <br />made in summer months; however, one trip was <br />scheduled in mid-April and one was in late Sep- <br />tember. Most of our collecting efforts were in <br />the mouths and lower reaches of the various tribu- <br />taries. <br /> <br />The flow of the Colorado River through the <br />Grand Canyon has been severely modified by the <br />closure of Glen Canyon Dam in 1963. The seasonal <br />floods and fluctuations of the river are now re- <br />placed with variations in water levels which <br />correspond to the generation of electricity. The <br />natural temperature regime has also been modified <br />as the water is discharged from the lower portion <br />of the dam. During our study the water tempera- <br />ture of the Colorado River was consistently 100C <br />or colder in the upper portion of the river and <br />gradually warmed to a high of 160C 250 miles down- <br />stream. Tributary temperatures varied with the <br />seasons. The still waters behind Glen Canyon Dam <br />act as a silt trap for the normally turbid river, <br />thus the present discharge from the dam is ex- <br />tremely clear. <br /> <br />Fish collections were obtained from thirty- <br />five different sites along 280 miles of the Colo- <br />rado River in Coconino and Mohave counties in Ari- <br />zona. A total of 112 collections was obtained <br />between September 1970 and June 1976. Nineteen <br />species of fishes were represented of which fif- <br />teen (79%) were introduced (exotics). The four <br />native fishes were the humpback chub, Gila cypha, <br />speckled dace, Rhinichthys osculus, flannelmouth <br />sucker, Catostomus latipinnis, and blue head suck- <br />er, Pantosteus discobolus. In addition to the <br />nineteen species two different hybrid combina- <br />tions were taken: the sucker hybrid Catostomus <br />latipinnis x Xyrauchen texanus and various crosses <br /> <br />IGrand Canyon National Park, Colorado River <br />Research Series: Contribution No. 24; and <br />Tulane University, Museum of Natural History: <br />Contribution No. 10. <br /> <br />2Tulane University, New Orleans, Louisiana. <br /> <br />3M ississippi State University, State College, <br />Mississippi. 599 <br /> <br />of the rainbow trout, Salmo gairdneri with other <br />species of trout. We presume the hybrid trout <br />were artificially produced at some hatchery and <br />then stocked in the canyon area. <br /> <br />In comparison to many Eastern rivers (50 to <br />150 species) the Colorado River could not be con- <br />sidered as species rich even before impoundment. <br />Perhaps eight or as many as ten species once <br />lived in the Grand Canyon area of the Colorado <br />River. However few, most of the forms are unique <br />and most occur nowhere naturally outside of the <br />Colorado basin. <br /> <br />Three of the four native fishes found in the <br />area seem to be maintaining adequate populations. <br />Perhaps their success is due to their ability to <br />utilize a number of small tributaries as well as <br />the larger tributaries for spawning. These three <br />species are the speckled dace, Rhinichthys oscu- <br />ius, flannelmouth sucker, Catostomus latipinnis, <br />and the bluehead sucker, Pantosteus discobolus. <br /> <br />The flannelmouth sucker, Catostomus latipin- <br />nis (Figure 1, upper), is widespread in the Colo- <br />rado River system and it was collected from sites <br />throughout the Grand Canyon area, i.e., from <br />Lee's Ferry downstream to the upper end of the <br />Mead Reservoir. Adult, young or both were taken <br />from fourteen tributaries and from nine sites <br />along the main channel of the Colorado River. <br /> <br />The main channel of the Colorado River prob- <br />ably provided more spawning area prior to im- <br />poundment than it does now. Although we <br />assume that some spawning takes place in the main <br />stream we did not record direct evidence. All <br />spawning activities that we observed were in the <br />lower sections of tributary streams. In general <br />the flannelmouth sucker spawning period extends <br />from March to late May in the Grand Canyon area. <br /> <br />On February 29, 1976 reproductive condition <br />of the flannelmouth sucker was checked at the <br />mouth of the Paria River. Male individuals var- <br />ied from a silvery color to orange-salmon color <br />on body and fins. The silvery colored (prenup- <br />tial) individuals had slightly developed tuber- <br />cles. Those males with orange-salmon breeding <br />color had moderately developed breeding tubercles. <br />A few of these males were ripe, i.e., they voided <br />milt upon slight pressure but none was "running" <br />ripe. Most females were robust but none was <br />ripe. The paria River was 13.50C and the main <br />Colorado River just off the mouth of the paria <br />was 70C. The Paria is invariably turbid and thus <br />precludes direct observations. <br /> <br />On April 3, 1976 collections and observations <br />were made at the paria River. The paria at the <br />cOllecting site was 180C and the main Colorado was <br />8.50C. One "running" ripe male Catostomus lati- <br />pinnis was collected. It had well developed tuber- <br />cles. Non-ripe females were collected although <br />most had bright orange-tangerine color on lower <br />fins including lower half of caudal fin. <br /> <br />Two ripe male flannelmouth suckers were collec- <br />ted on AprilS, 1976 from the paria River. These <br />two males had better developed tubercles than the <br />non-ripe males. No ripe female was taken al- <br />though most specimens had moderately developed <br />breeding colors. Two females were blackish or <br />grayish without any orange coloration. The Paria <br />