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,. <br />. ~ <br />~- <br />i , ~ ~k <br />~.,~. <br />~~~ <br />aF ~ <br />~' -a <br />~wr.-' <br />~' - <br />•~ -t~ d <br />.T ~. <br />.h 1~ f <br />h;~r _", <br />~~-~.:- <br />'4 I <br />~{ <br />1, <br />If <br />,I <br />~I <br />1 <br />ri <br />Notropis lutrensis, has seemingly re- <br />placed it throughout that system (Fig. <br />2A). The red shiner spreads rapidly, <br />naturally and from fishermen's bait <br />buckets. In view of this, and of pro- <br />posals to build the Charleston Dam on <br />the upper San Pedro River and the <br />Hooker Dam on the Gila River in New <br />Mexico, the outlook for Meda appears <br />bleak. <br />The Gila topminnow, Poecfliopsis <br />occfdentalis, provides another example <br />of the influence of an exotic fish on a <br />native species. The Gila topminnow <br />also was at Tempe in 1890, where it <br />undoubtedly lived in marshes along the <br />1 <br />stream rather than in the channel itself. <br />Records show that this fish ranged from <br />a high•elevation habitat adjacent to <br />Frisco Hot Spring in western New <br />Mexico (27) to an area near Dome, <br />Arizona (28). These, plus records from <br />most of the central and southern parts <br />of the Gila basin (Fig. 3), leave no <br />doubt that the topminnow once lived <br />throughout the Gila drainage, and per- <br />haps in suitable habitats along-the lower <br />Colorado as well. Its decline was rapid. <br />Gila topminnows were considered by <br />Hubbs and Miller (28) to be "one of the <br />commonest fishes in the southern part <br />of the Colorado River drainage." Today <br /> <br />rl,•~ ~. ~~, A <br />tY!r ~r r, <br />'•; ti, t '~... GILA RIVER BASIN, <br />;~ <br />~. }. ~ %~ .. .,! ., ~' AR120NA, NEW MEXICO. AND SpgR4 <br /> <br />' <br />t. it •.. .., w -^ •,; -/ <br /> <br /> <br /> <br /> <br /> <br /> <br />B <br />~•, <br />L i ~' <br />. •~•• 1 -• - - , <br />```` _ <br />..\ • <br />. _ `_-~'. <br />-- -- -_._ .0~~-.-..--~- • - - ~ - <br />Fig. 3. ~ A 1 Present distribution of the introJaec~ reLl shiner in the Giia Ricer basin. <br />It3) Present and p,l~t diaributiun of :h~• natnc Gila ,pinedace in the Gila Ri\~er basin. <br />Open circles are Lx:liities ,,i larme~ o.curren~e v.herc the pre,ent absence of the fish <br />has been ,~~ntirmed: h:df-,c~li;l circles ;. r; Inc,litie~ that tic hate Writ ree\:Im.n~d: :ohLi <br />circles :Ire ioc~litie, ~~•here the ~~ined::cr pei,i~t,. <br />tai. <br />the fish persists only in one spring area <br />in Santa Cruz County, Arizona. <br />The diminution in the range of this <br />fish is attributable in part to desiccation <br />of habitat, especially in places like the <br />lower Gila River. Arroyo cutting iq the <br />1880's (4, 29), must have destroyed <br />much of its preferred quiet-water habi- <br />tat even before man began to use the <br />water. The introduction and spread of <br />the mosquito fish, Gambusia minis; <br />throughout most of the basin over the <br />last 40 years appears to,y~e been the <br />most important factor, however, in the <br />overall decline of the native fish. The <br />aggressive Gambusia has played a part <br />in the decline of a number of fishes is <br />the West and in the destruction of popu. <br />lations of fishes in other areas (3f~}, Ir <br />the bes"t-documented examples ct re. <br />placement of Poeciliopsis by Gami,t~s~a <br />the sequence is rapid. In the forrurl} <br />fishless Arivaca Creek, in Arizona. top <br />minnows were introduced in 19= ;. Ir <br />1957 they were extremely common, `gut <br />in 1959, mosquito fish of unknowr <br />origin had totally reglaced them (4) <br />The sequence was similar in an artesian <br />spring area near Safford, Arizona. Gilt <br />topminnows abounded in canals anc <br />ponds of that area in 1962. In 1963 <br />specimens of Gambusia were taken it <br />the area, and in the same pond at <br />Poeciliopsis. In our intensive survey <br />only the introduced mosquito fish way <br />found in 1966.- Restriction to a single <br />isolated drainage seems a precarious <br />position for the Gila topminnow; thi <br />formerly abundant, endemic species <br />now qualifies for category 4, ever <br />though it was originally acategory--: <br />species. <br />In discussing fishes in category 4, evc <br />use as examples species naturally iso <br />lated in aquatic systems of closed basins <br />or isolated, by habitat preference of <br />ph}~siological attributes, or both, tc <br />springs or springlike environments <br />Alterations induced by man,. a major <br />cause of declining populations in Bate <br />gories 2 through 4, are particularly im <br />portant to fishes in category 4. Minot <br />changes in a small spring, for example <br />may influence the entire population of t <br />species. The acute susceptibility of sucl <br />fortns to catastrophe is evident in the <br />recent compilations of extinct fishes o <br />the United States (?, 4}; three of the sip <br />fishes li>ted were in restricted waters it <br />Nevada, and a fourth, C~~prinodor <br />borinus, was in an isolated spring it <br />Texas. <br />Emnetri~hth}•s nrerriami, the Asl <br />Meadows killifi=h, one of the tac <br />know n species of the c~ prinodoot genu• <br />sc rt=tvice, vot.. ts• <br />