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<br />. lqq3 SeDp~sl\oV\~ <br /> <br />Transactions of the American Fisheries Society 122:599~08. 1993 <br /> <br />.. <br /> <br />tILl 7 <br /> <br />Interactions between Native and Nonnative Fishes of the <br />Upper Muddy River, Nevada <br /> <br />G. GARY SCOPPETTONE <br /> <br />U.S. Fish a.nd Wildlife Service, National Fisheries Research Center <br />Reno Substatj.~n, 4600 Kietzke Lane. C-l20, Reno. Nevada 89502, USA <br /> <br />Abstract.-I investigated interactions between native and nonnative fishes in the upper Muddy <br />River system to add insight into (I) the mechanism causing the decline of the Moapa dace Moapa <br />coriacea after the introduction of the shortfin mony Poecilia mexicana, (2) the reason Moapa White <br />River springfish Crenichthys baileyi moapae were less affected by the introduction, and (3) the <br />reason interactions between natives is relatively benign. I investigated the hypothesis that the <br />shortfin mony caused the decline of the Moapa dace through competition or predation on larvae, <br />pressures not experienced by the Moapa White River springfish. Relative interspecific competition <br />was analyzed by contrasting the ranges of spatial and dietary overlap among larval, juvenile, and <br />adult life stages. There appeared to be moderate to low spatial overlap between the various life <br />stages of native and nonnative fishes. Overlap in diet was highest between adult Moapa White <br />River springfish and shortfin mollies. Laboratory experiments suggested that shortfin monies prey <br />vigorously upon fish larvae. In terms of spatial habitat use, Moapa White River springfish larvae <br />were less available to adult shortfin mollies for consumption than were Moapa dace larvae. When <br />predatio,n on larvae is the mechanism by which nonnative fish reduce native forms, aggressiveness <br />of the predator and the degree to which the predator overlaps in habitat with the prey may influence <br />the degree to which a native fish population is affected. <br /> <br />The addition of nonnative fish species may <br />greatly alter the structure of a native fish com- <br />munity (Moyle et al. 1986; Brown and Moyle <br />1991). Frequently, nonnative fishes replace or <br />greatly diminish natives, and several western spe- <br />cies are extinct or have experienced dramatic de- <br />clines following the invasion of nonnative fishes <br />(Miller et al. 1989; Moyle and Williams 1990). <br />The mechanisms of these adverse interspecific in- <br />teractions have received little attention (Moyle et <br />al. 1986; Ross 1991). <br />After the upper Muddy River, Nevada, was in- <br />vaded by nonnative fishes, the two native fishes, <br />Moapa dace Moapa coriacea and Moapa White <br />River springfish Crenichthys baileyi moapae, de- <br />clined (Cross 1976). The Moapa dace declined suf- <br />ficiently that it was federally listed as endangered <br />(U.S. Department of the Interior 1973). The Mo- <br />apa White River springfish also .declined but less <br />dramatically, and it is a candidate 2 species (being <br />considered for listing as endangered or threatened; <br />U.S. Fish and Wildlife Service 1991). <br />Both species are endemic to the headwaters of <br />the Muddy River (also called the Moapa River), <br />Clark County, Nevada, a tributary to the Colo- <br />rado River system. The river originates from about <br />20 warm springs (31.0--32.0oC at their sources) <br />having a combined discharge of 1.1 m3/s (Eakin <br />1964). Water cools in a downstream direction. <br />Moapa dace and Moapa White River springfish <br />are thermophilic, restricted to temperatures be- <br /> <br />tween 26.0 and 32.0oC. They are hence relegated <br />to the upper 2 km of the approximately 40-km <br />river and to several small headwater tributaries <br />(Deacon and Bradley 1972; Cross 1976; Scoppet- <br />tone et al. 1992). The general area in which they <br />occur is known as the Warm Springs area (Hubbs <br />and Miller 1948; La Rivers 1962). Reproduction <br />occurs year-round and is confined to the upper, <br />spring-fed tributaries, typically within 150 m of <br />the warmwater discharges (Scoppettone et al. <br />1992). In these areas, water temperatures vary be- <br />tween 29.0 and 32.20C and dissolved oxygen con- <br />centrations vary between 4.1 and 6.2 mglL, both <br />seasonally and over 24-h periods; conductivity is <br />about 964 /-Ls/cm and pH is 7.5 (my unpublished <br />data). Juveniles are found almost exclusively in <br />the spring-fed tributarie~, whereas adults are also <br />found in the main stem (Scoppettone et al. 1992). <br />There is little published information pertaining <br />to the life history of Moapa White River spring- <br />fish. Other subspecies of C. baileyi are omnivo- <br />rous and opportunistic in diet (Williams and Wil- <br />liams 1982) and withstand unusual extremes in <br />temperature and dissolved oxygen (Sumner and <br />Sargent 1940; Hubbs and Hettler 1964; Hubbs et <br />al. 1967). White River springfish reproduce year- <br />round, laying eggs 1.9 mm in diameter that are <br />typically attached to aquatic vegetation (Kopec <br />1949; Espinosa 1968). Their daily activity pat- <br />terns were studied by Deacon and Wilson (1967). <br />Two other, nonthermophilic, native fishes oc- <br /> <br />599 <br />