<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 />.
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