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<br />28 <br /> <br />GREAT BASIN NATURALIST <br /> <br />Vol. 48, No, 1 <br /> <br />upstream of the confluence (13-km reach), <br />and none of 25 individuals of the same three <br />species collected there had consumed crick- <br />ets, <br /> <br />DISCUSSION <br /> <br />Mormon Crickets and Stream Ecology <br /> <br />The movements of large bands of Mormon <br />crickets into the Green and Yampa rivers in <br />DNM in 1986 and 1987 provided a substantial <br />and high-quality organic input to this system. <br />This must have been the case in other years of <br />major outbreaks, such as from 1980 to 1987 in <br />DNM (Capinera and MacVean 1987, National <br />Park Service 1986). Mormon cricket availabil- <br />ity may be important to the ecology of both <br />native and nonnative fishes, This is especially <br />true in DNM, which contains the only known <br />spawning site for the endangered humpback <br />chub in the Green River Basin, and one of the <br />two confirmed spawning sites for the endan- <br />gered Colorado squawfish (Tyus et al. 1987). <br />Various investigators have studied Green <br />River fishes (Holden and Stalnaker 1975, <br />Miller 1964, Miller et al. 1982, Vanicek and <br />Kramer 1969) with emphasis on rare, native <br />species listed or considered for listing as <br />threatened or endangered (U.S. Department <br />of the Interior 1985). The fauna also includes <br />numerous nonnative fishes introduced for <br />sport, forage, food, or by accident (Tyus et al. <br />1982), Food habits of native fishes are gener- <br />ally known (Vanicek and Kramer 1969, Jacobi <br />and Jacobi 1982), but their seasonal use of <br />terrestrial animals is not, Foods of nonnative <br />species are described for other rivers (e.g" <br />Carlander 1977), but few data exist in DNM, <br />Mormon cricket movements into rivers in <br />DNM in spring provide food for stream fishes. <br />This is a time when flooding, scouring, and <br />annual insect emergence reduce food <br />availability, High-water turbidity presumably <br />reduces visual feeding efficiency of predatory <br />fishes, yet large numbers of crickets at or near <br />the water surface are vulnerable to aquatic <br />predators, Cricket availability coincides with <br />prereproductive periods for some native spe- <br />cies, including round tail and humpback <br />chubs, flannelmouth sucker, and Colorado <br />squawfish, As reported by Defoliart et al. <br />(1982), adult Mormon crickets have a mean <br />crude protein content of 58% and a fat content <br />of 16,5%, Such abundant and high-quality <br /> <br />food might enhance fish reproductive success, <br />postreproductive recovery, or both, <br />We do not advocate that native fishes time <br />reproductive behavior to cricket input. How- <br />ever, a demonstrable relationship between <br />nutrition and reproductive success in these <br />fishes would be of interest, and long-lived <br />fishes could incorporate such unpredictable <br />major outbreaks to advantage in life-history <br />strategies (Smith 1981, Tyus 1986), Longevi- <br />ties of endemic Colorado River fishes studied <br />to date indicate long life is an exceptional <br />attribute of this fauna, Bony tail chub (Gila <br />elegans) older than 40 years have been re- <br />ported, razorback sucker (Xyrauchen tex- <br />anus) commonly reach 30 to 40 years, and <br />Colorado squawfish that formerly achieved <br />L 8 m in length must have lived even longer <br />(McCarthy and Minckley 1987, Rinne et al. <br />1986). Periodic outbreaks of Mormon crickets <br />could contribute significantly to nutrition, di- <br />rectly or indirectly, for a number of consecu- <br />tive or disjunct years during such a long pe- <br />riod oflife, <br />High flows and seasonal flooding in the <br />mainstream Green River are now reduced by <br />dams (Joseph et al. 1977). This alters or pre- <br />cludes floodplain inundation and removes <br />particulate organics through reservoir entrap- <br />ment (e, g., Minckley and Rinne 1986), <br />Flooded lowlands were formerly expansive <br />during sustained high flows, which often ex- <br />ceeded mean discharge (181 m3/second, based <br />on an 86-year record at Jensen, Utah) by more <br />than an order of magnitude during snowmelt <br />(Remilliard et al. 1986), Floodplain communi- <br />ties were thus made available to predation by <br />riverine fishes, as observed elsewhere <br />(Welcomme 1979). In the Green River, Colo- <br />rado squawfish and razorback sucker have <br />been radio tracked to flooded lowlands, where <br />they presumably feed (Tyus 1987, Tyus et al. <br />1987), Flood reduction and loss of al- <br />lochthonous inputs may make seasonal inputs <br />of terrestrial animals, including Mormon <br />crickets, more important now than histori- <br />cally. <br /> <br />Mormon Cricket Control <br /> <br />In their natural grassland or sagebrush- <br />dominated habitats, Mormon crickets prefer <br />to feed on succulent, herbaceous vegetation, <br />Damage to range grasses is considered so <br />slight that they are not generally considered a <br /> <br />. <br />\ <br /> <br />... <br />