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<br />VII, DESERT FISHES
<br />
<br />455
<br />
<br />ered by sedimenting muds (Moore, 1944b). A number of large cyprinid
<br />fishes in rivers of Eurasia spawn similarly, and it is suggested that this
<br />type of behavior also makes the pelagic eggs less conspicuous to predators
<br />(Nikolsky, 1963). In Australian rivers, silver perch (Bidyanus bidyanus;
<br />family Theraponidae) and golden perch (PlectropUtes ambiguus; family
<br />Serranidae) spawn with the same kind of timing to floods (Lake, 1967).
<br />The stimulus of water-level changes, or related factors, in the reproduc-
<br />tion of many large-river fishes is well documented. North American
<br />buffalo fishes (genu:; Ictiobus) are notorious for this feature (Yeager,
<br />1936). Van Ihering,(1935) reports it for several South American species,
<br />Boulenger (1907) for numerous fishes of the Nile, and Hora (1945) re-
<br />lated water-level changes and phases of the moon as stimuli for certain
<br />Indian cyprinids. Some fishes of desert lakes, such as the cui-ui (Chas-
<br />mistes cujus) of Pyramid Lake, Nevada, move into influent streams to
<br />spawn in spring. Changes in river level strand many eggs, young, and even
<br />adults, to die on gravel bars (Snyder, 1917; LaRivers, 1962).
<br />Fishes characteristic of the lower ends of large desert rivers, as elsewhere,
<br />may depend upon periodic flooding of marginal habitats for their reproduc-
<br />tive activities or for feeding by themselves or by their young. The nutrients
<br />on fertile floodplains stimulate rapid development of plankton, not to
<br />mention the provision of a vast volume of terrestrial organic material
<br />(Evans-Prichard, 1940; Stubbs, 1949; Hickling, 1961; Nikolsky, 1963).
<br />Beheading of many desert streams by dams has had a profound effect on
<br />these and other lower-river fishes.
<br />Some forms such as the massive Colorado River squawfish seem to
<br />have performed upstream "runs" prior to damming (Dill, 1944; Miller,
<br />1961a), and the physical barriers may have blocked a critical stage in that
<br />species' life cycle (as it does in salmonids, such as Oncorhynchus spp.,
<br />and other fishes that run into rivers from tbe sea to spawn).
<br />On the other hand, changes in a myriad of other factors has been evi-
<br />denced by alterations of the entire fauna of the Colorado system. Vanicek
<br />et aI. (1970) have impressively documented the absence of reproduction
<br />by indigenous fishes in a 105-km reach of the Green River, Utah, below
<br />Flaming Gorge Dam. This was attributed to lowered water temperatures
<br />in summer periods of high discharge of water from the lake's hypolimnion.
<br />" Below the mouth of the Yampa River. a major tributary of the Green,
<br />conditions resembled those existing prior to the dam, and native fishes re-
<br />produced successfully. Sexual activities of aU the larger cyprinids (Squaw-
<br />fish and Gila spp,) seemed closely related to peak water temperatures and
<br />a decline in volume of flow (V anicck and Kramer, 1969). Reproduction
<br />of these fishes at inception of low discharge and by the "s.and shiner
<br />(Notropis stramineus) in the western part of the Great Plains (Summerfelt
<br />
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