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<br />. .1:, <br /> <br />i qq3 ~m (en) ef at. <br /> <br />Nonh Amertcan Journal of Fisheries Management 13:467-474. 1993 <br /> <br />~7'1'+IO'3S <br /> <br />9) 7g~. <br /> <br />t <br /> <br />Probabalistic Projections for Recovery of the <br /> <br />Endangered Cui-ui <br /> <br />JOHN M. EMLEN <br /> <br />National Fisheries Research Center, U.S. Fish and Wildlife Service <br />Naval Station Puget Sound, Seattle, Washington 98115, USA <br /> <br />THOMAS A. STREKAL <br /> <br />U.s. Bureau of Indian Affairs <br />1677 Hot Springs Road, Carson City, Nevada 89706, USA <br /> <br />CHESTER C. BUCHANAN <br /> <br />U.S. Fish and Wildlife Service <br />4600 Kietzke Lane, Building C. Reno, Nevada 89502, USA <br /> <br />Abstract. - The cui-ui Chamistes cujus, a lake sucker found in only Pyramid Lake, Nevada, is <br />listed as endangered under the U.S. Endangered Species Act, and a recovery plan has been for- <br />mulated in an effort to save it. We used a population simulation model that incorporated envi- <br />ronmental stochasticity in water availability to project the persistence of cui-ui over 200 years. <br />Based on this approach, recovery of the species in terms of persistence was evaluated for the existing <br />hydrological situation and for situations involving water supplementation in various amounts. Our <br />calculations indicate that immediate (as of spring 1991) aCQuisition of 70,000 acre-feet per year <br />of supplemental water to raise levels in Pyramid Lake would have assured recovery and persistence <br />over 200 years with a probability of 0.95. Postponement of acquisition for 3 years followed by <br />incremental increases of 3,000 or 10,000 acre-feet per year would require, respectively, 83,000 and <br />120,000 acre-feet of annual supplemental water to assure persistence. The approach is applicable <br />to a wide range of species and conditions. <br /> <br />The U.S. Endangered Species Act of 1973, as <br />amended, provides that "the Secretary of the In- <br />terior shall develop and implement plans for the <br />conservation and survival of endangered species <br />and threatened species.. .." To carry out this <br />charge, recovery teams set up under the Act collate <br />life history data and produce recovery plans. Ide- <br />ally, the information available to these teams <br />should be sufficient to project hypothetical future <br />population densities under various feasible man- <br />agement scenarios. In this way, the effectiveness <br />and cost of specific potential recovery actions can <br />be evaluated. <br />The cui-ui Chasmistes cujus is a large omniv- <br />orous sucker (family Catostomidae) unique to Pyr- <br />amid Lake, Nevada, and is an obligate stream <br />spawner in the lower portion of the Truckee River. <br />Each spring, adults congregate in a prespawning <br />aggregate near the mouth of the river and, ifinftow, <br />river access, and water temperature are suitable, <br />migrate into the river to spawn over gravel sub- <br />strate (Scoppettone et al. 1983). Upon completion <br />of spawning, adults return to the lake and do not <br />spawn again until some subsequent spring. The <br />fish appear to attempt spawning annually, but un- <br />der present conditions may be able to ascend the <br /> <br />river only two or three times a decade. Life span <br />reaches 41 years, and females generally outlive <br />males, resulting in an increasingly skewed sex ratio <br />with age (Scoppettone 1988). <br />Each cui-ui female produces 40,000-180,000 <br />eggs annually, the number increasing with female <br />size and generally with age. Fertilized eggs hatch <br />in 1-2 weeks. Yolk-sac larvae remain in the gravel <br />substrate an additional 5-10 days before emerging <br />and then emigrate downstream into the lake. More <br />information on cui-ui life history can be found <br />in Koch (1972), Chatto (1979), Scoppettone et al. <br />(1982, 1983, 1986), Sigler et al. (1985), and Bu- <br />chanan and Coleman (1987). Information dis- <br />cussed below is from these sources. <br />Size of the historical cui-ui populations and <br />spawning runs is not known; only general obser- <br />vations have been reported. For example, Snyder <br />(1917) noted that "at times cui-ui appeared in such <br />large and densely packed schools [in the Truckee <br />River] that considerable numbers were crowded <br />out of the water in shallow places. . . ." From such <br />descriptions, and the fact that spawning runs not <br />only used to feed many people but provided a <br />cultural basis for the local Paiutes, we may rea- <br />sonably conclude that spawning runs probably <br /> <br />467 <br /> <br />8pp. <br />