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<br />
<br />The cui-ui (Chasmistes cujus) is a federally listed
<br />endangered species endemic to Pyramid Lake,
<br />Nevada. The species is believed to be the last
<br />remaining genetically pure member of the genus
<br />Chasmistes (Miller and Smith 1981). This taxonomic
<br />distinction, the severe decline of the cui-ui popula-
<br />tion, and the favorable outlook for recovery of the
<br />species resulted in its receiving a top priority rating
<br />for recovery (U.S. Fish and Wildlife Service 1983).
<br />Because much natural history information was
<br />lacking, the Service supported a 4-year study of the
<br />species as outlined in the Cui-ui Recovery Plan
<br />(U.S. Fish and Wildlife Service 1978), We present
<br />the results of that research.
<br />The primary cause of the decline of the Pyramid
<br />Lake cui-ui population was clearly the disruption of
<br />the reproductive cycle. During the past 50 years,
<br />spawning adults have had only restricted access to
<br />the Truckee River, the only permanent tributary of
<br />Pyramid Lake, An extensive and shallow delta that
<br />formed at the mouth of the river in the 1930's has
<br />been a barrier to migrating adults in most years since
<br />then. The delta resulted from a drastic lowering of
<br />the water level of Pyramid Lake over a relatively
<br />short period, as a result of water diversion from the
<br />Truckee River. The water level of the lake dropped
<br />about 25 m between 1906 and 1982. The comple-
<br />tion of the Newlands Project in 1905 (Townley
<br />1977) and the associated construction of Derby Dam
<br />diverted an average of 311 million m3 annually, or
<br />about half the river flow.
<br />A series of measures were taken, beginning in the
<br />mid-1970's, to attempt to restore the Pyramid Lake
<br />sport and Indian food fishery. In 1976, Marble Bluff
<br />Dam and Pyramid Lake Fishway, a canal 4.8 km
<br />long that bypasses the delta, were completed. The
<br />dam diverts water down the fishway, enabling
<br />migrating fish to bypass the delta. Also, portions of
<br />the water stored in Stampede Reservoir (an
<br />impoundment on a tributary of the Truckee River)
<br />were reserved to augment flows required for cui-ui
<br />spawning.
<br />As a further measure against the possibility of
<br />extinction, hatchery propagation of cui-ui for
<br />release into Pyramid Lake was begun in 1973, based
<br />on techniques developed by Koch and Contreras
<br />(1973). A fully equipped cui-ui hatchery, managed
<br />and maintained by the Pyramid Lake Paiute Indian
<br />Tribe, produced an average of 7 million cui-ui larvae
<br />annually in 1980-84 (Alan Ruger, Pyramid Lake
<br />Fisheries, personal communication). These larvae
<br />
<br />were released into the lower Truckee River or
<br />directly into the lake,
<br />In 1981, the U.S. Fish and Wildlife Service (Seattle
<br />National Fishery Research Center and Reno Great
<br />Basin Complex Office) began the present study to
<br />provide life history information that might facilitate
<br />recovery of the species. Adult cui-ui, taken on their
<br />spawning migration, were confined in a natural
<br />braid of the lower Truckee River (Scoppettone et
<br />al. 1983). Data developed on cui-ui reproduction
<br />here, under controlled conditions, served as the
<br />basis for the rest of the work in the main stem of
<br />the Truckee River. The phase of the life history
<br />spent in the river was emphasized because of its
<br />obvious importance in determining survival of the
<br />species. Included in the work were studies of
<br />spawning migration, reproduction, emigration of
<br />larvae, age and growth, population size, and food.
<br />Each spring, adult cui-ui congregate at the south
<br />or river end of Pyramid Lake before they migrate
<br />upstream to spawn (La Rivers 1962). The concen-
<br />tration is greatest near the mouth of the river (Koch
<br />1972). Catches per unit of effort in gill nets fished
<br />in Pyramid Lake near the Truckee River and the
<br />Pyramid Lake Fishway were greatest when river
<br />flows were high (SonnevilI981). Historically, cui-ui
<br />spawned from mid-April to late May, primarily in
<br />the lower 40 km of stream (Snyder 1918). In more
<br />recent years, spawning was observed in Pyramid
<br />Lake itself from May through July Oohnson 1958;
<br />La Rivers 1962; Koch 1973). However, the high
<br />salinity in the lake is lethal to incubating eggs
<br />(Chatto 1979). Even the hatching success of eggs
<br />deposited at a freshwater inlet was questionable
<br />(Koch 1973). In the river, adult cui-ui spawned in
<br />riffles over predominantly gravel substrate, burying
<br />their adhesive, demersal eggs at depths as great as
<br />10 cm (Snyder 1918; Scoppettone et al. 1983).
<br />Cui-ui spawning behavior was described by
<br />Scoppettone et al. (1983), early life stages by Koch
<br />(1972), and embryology by Bres (1978). At lOoC,
<br />eggs hatch in 13 days and larvae swim-up about
<br />5 days after hatching (Koch 1972; Koch and
<br />Contreras 1973). Bres (1978) observed that the
<br />mouth of cui-ui larvae opened 16 days after
<br />hatching.
<br />When not congregated at the river end of the lake,
<br />adult cui-ui live primarily in littoral waters less than
<br />23 m deep Oohnson 1958; Vigg 1980), Zooplank-
<br />ton (not further identified) was reported to be the
<br />primary food of adults Oohnson 1958; La Rivers
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