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<br />472 <br /> <br />EMLEN ET AL. <br /> <br />1.0 <br /> <br />(I) <br />... <br />CU <br />Q) <br />>- <br />o <br />o <br />C\/ <br />C) <br />c: <br />+= <br />(I) <br />'Cij <br />... <br />Q) <br />Q. <br />- <br />o <br />>- <br />- <br />:s <br />CU <br />..0 <br />o <br />... <br />a.. <br /> <br />delist <br /> <br /> <br />--------------------------------- <br /> <br />_.-" <br />-.-" <br /> <br />0.9 <br /> <br />10.000 acre-feet increments <br /> <br /> <br />rec lassify <br /> <br />'" <br /> <br />'" <br />--~r----------------------------- <br />'" <br /> <br />-'" <br /> <br />3,000 acre-feet increments <br /> <br />'" <br /> <br />0.8 <br /> <br />0.7 <br />o <br /> <br />~ ~ ~ ~ 100 <br />Supplementary water (x1 ,000 acre-feet) <br /> <br />120 <br /> <br />FIGURE 2.-Probability of cui-ui population persistence (over 200 years) as a function of supplemental water <br />when water acquisition begins in 1994 and rises in yearly increments of 3,000 or 10,000 acre-feet. cui-ui could be <br />"de listed" as endangered at 0.95 probability of persistence or reclassified as threatened at 0.85 probability of <br />persistence. <br /> <br />vat ion measures listed in the recovery plan should <br />become mandatory (Strekal et at. 1992). At an 85% <br />probability of persistence , the IO,OOO-acre-foot in- <br />crement scenario leads to an eventual yearly level <br />of about 40,000 acre-feet (reachable by 1998), and <br />the 3,OOO-acre-foot increment program would <br />ultimately require about 50,000 acre-feet yearly <br />(reachable by 20 II) to achieve reclassification. <br /> <br />Discussion and Conclusion <br /> <br />The uncertainty in the amount of required sup- <br />plemental water, illustrated by the gap between <br />the upper and lower curves in Figure I, demon- <br />strates the critical need for better information on <br />early survival of the cui-ui. Model results should <br />be updated and refined as better estimates of sur- <br />vival become available. For the moment, we must <br />make do with the data we have. With this caveat, <br />two conclusions can be made. <br />First, acquisition of supplemental water before <br />the spring aggregation in 1991 in the amount (best <br />estimate) of 70,000 acre-feet would have led to <br />conditions allowing for eventual (after response <br />has been checked and documented) declassifica- <br />tion of the cui-ui. <br /> <br />Second, as the acquisition of supplemental wa- <br />ter becomes increasingly protracted, larger acqui- <br />sitions become necessary, delisting is progressively <br />postponed, and the risk of coincidental extinction <br />grows. If water acquisition were to begin in spring <br />1994 with 5,000 or fewer acre-feet per year and <br />incremented yearly by less than 5,000 additional <br />acre-feet per year, the eventual yearly input of sup- <br />plemental water required for recovery (interpo- <br />lated from Figure 2) would exceed realistic limits <br />on availability, making imposition of other con- <br />servation measures necessary. <br /> <br />References <br /> <br />Buchanan, C. c., and M. E. Coleman. 1987. The cui- <br />ui. Pages 425-436 in R. L. DiSilvestro, editor. Au- <br />dubon Wildlife Report. Academic Press, Orlando, <br />Florida. <br />Buchanan, C. c., and T. A. Strekal. 1988. Simulated <br />water management and evaluation procedures for <br />cui-ui (Chasmistes cujus). U.S. Fish and Wildlife <br />Service and Bureau of Reclamation, Reno, Nevada. <br />Chatto, D. A. 1979. Effects of salinity on hatching suc- <br />cess of the cui-ui. Progressive Fish-Culturist 4 I :82- <br />85. <br />Coleman, M. E., D. Winkelman, and H. L. Burge. 1987. <br />