Laserfiche WebLink
<br />. . <br /> <br />Table 2, (continued) <br /> <br />FAMILY <br />species <br /> <br />Common name <br /> <br />Distribution <br /> <br />Habitat <br /> <br />PERCICHTHYIDAE <br />Morone chrywps <br />(Rafinesque) <br /> <br />Morone mississippiensis <br />lordan & Eigenmann <br /> <br />Morone saxatilis <br />(Walbaum) <br /> <br />CENTRARCHIDAE <br />Lepomis cyanellus <br />Ralinesque <br /> <br />Lepomis gulosus <br />(Cuvier) <br /> <br />Lepomis macrochirus <br />(Rafinesque) <br /> <br />Lepomis microlophus <br />(Giinther) <br /> <br />Micropterus dolomieui <br />Lacepede <br /> <br />Micropterus salmoides <br />(Lacepede) <br /> <br />Pomoxis annularis <br />Rafinesque <br /> <br />Pomoxis nigromaculatus <br />(Lesueur) <br /> <br />PERCIDAE <br />Etheostoma exile <br />(Girard) <br /> <br />Etheostoma nigrum <br />Rafinesque <br /> <br />Perea flavescens <br />(Mitchell) <br /> <br />Stizostedion vitreum <br />(Mitchell) <br /> <br />CICHLIDAE <br />Cichlasoma nigrofasdatum <br />(Giinther) <br /> <br />Cichlasoma severum <br />(Heckel) <br /> <br />Oreochromis mossambicus <br />(Peters) <br /> <br />Tilapia zilli <br />(Gervais) <br /> <br />396 <br /> <br />.~. <br /> <br />and the species is gone from the Verde River (Mello & Turner 1980), The sta tus <br />of Arizona trout (S. apache) also is of concern, and nearly all the endemic <br />desert-stream fish are in severe decline (Miller & Lowe 1977). The only viable <br />population of the desert pupfish, once the most common fish in the Southwest, <br />may be an undescribed subspecies isolated in Quitobaquito Spring in Organ <br />Pipe Cactus National Monument, Arizona (Kynard & Garrett 1976; Deacon <br />et al. 1979). Except for the speckled dace, the big-river fish have been extirpated <br />from the lower mainstream (Minck ley 1979), and humpback chub, speckled <br />dace, bluehead, flannelmouth and perhaps razorback suckers are the only <br />endemics extant in the Grand Canyon (Carothers & Minckley 1981; Carothers <br />& Johnson 1983). Razorback suckers are established and common in Lake <br />Mohave; bony tail chub are also present, but apparently not reproducing (Dr L. <br />Paulson, Univ. Nevada at Las Vegas, pers, commun.). Dams in the Upper Basin <br />have eliminated or adversely affected the native fish for long distances down- <br />stream (cf. Vanicek et al. 1970; Holden 1979; Stanford & Ward 1984). Only a <br />few isolated canyon habitats (e.g. Yampa River Canyon: Vanicek et aI, 1970) or <br />unregulated tributaries (e.g. White River: Lanigan & Berry 1981) contain an <br />assemblage of native fish like the pristine river fauna (Table 1), All the native <br />big-river fish, except speckled dace and flannelmouth sucker, face extinction <br />(Tyus et at, 1982). <br />The major causes of the decline relate to loss of riverine habitat and inter- <br />actions with exotic species. More than one-quarter of the river has been con- <br />verted to lentic habitats by impoundment (Bishop & Porcella 1980). Fish <br />adapted for the turbid habitats of the main river have not survived in reservoirs, <br />with the possible exception of razorback suckers (Kimsey 1957; Minckley 1979; <br />Holden & Wick 1982). Regulated flows have armoured the river bottom in <br />tailwaters, and most of the crucial backwaters and marshes no longer receive <br />water. The thermal regime and trophic structure of remaining river segments <br />have been changed by releases from reservoirs. Diversions and pumping of <br />groundwaters have dried out many desert streams (e.g. lower Gila River: cf. <br />Holden 1979) and springs (Naiman 1981). However, Minckley (I 979) points out <br />that even these abrupt changes are no more severe, and perhaps are less general, <br />than climatic changes which have occurred in the recent history of the basin: <br />since the Pliocene, most of the native fauna has endured successive pluvial <br />episodes followed by desertification. But at no time were the native fish confronted <br />with numerous introductions of highly competitive, exotic species, some carry- <br />ing alien diseases (cf. Holden 1979; Holden & Wick 1982; Deacon 1979; Carothers <br />& Minck1ey 1981). Presently more than 50 exotic fish, led by carp {Cyprinus <br />carpio), threadfin shad (Dorosoma petenense), rainbow trout (Salmo gairdneri) <br />and largemouth bass (Micropterus salmoides), are established in the basin <br /><Table 2), Others have been introduced but apparently are not reproducing <br />(Minckley 1973, 1979; Moyle 1976; Nicola 1979; Courtnay & Deacon 1983). <br />Exotic species prey on the eggs and juveniles of indigenous fish, and compete for <br />space and spawning sites (Deacon 1979), Thus, red shiners (Notropis lutrensis) <br />397 <br />