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296 <br />less than optimal, as they are in the upstream re- <br />gions of the historic range of Colorado squawfish. <br />Our observations suggest that the growth physi- <br />ology and timing of spawning of the Colorado <br />squawfish are not well adapted to the temperature <br />regimes of upper-basin rivers (cf. Keast 1985). <br />Nonetheless, the fish might have been common <br />here under former, pristine conditions because <br />early-life mortality then was relatively low and <br />these life-history characteristics were not impor- <br />tant impediments to population maintenance. <br />Lack of strong directional selection then may have <br />precluded evolution of phenotypes that grow more <br />rapidly or spawn earlier in the year under upper- <br />basin temperature regimes. <br />Management recommendations <br />ManagemenY~recommendations for this endan- <br />gered species are based on the arguments that we <br />have made and include possible tests of our hy- <br />pothesis. <br />Dams and reservoirs might be operated to in- <br />crease both the length of the growing season and <br />mx <br />Appendix. Computation of vital statistics for simulated populations of fast(F)-and slow(s)-growing Colorado squawfish that mature at 3 <br />and 6 years of age, respectively. It is assumed that, beginning in the first year of maturity and continuing through age 10, each <br />slow-growing female produces 0.5 mature female offspring annually and each fast-growing female produces 6.5-based on survival with <br />99% annual mortality in the smallest length class; see Table l.a <br />x !x <br />(age in years) <br />S F <br />the availability of temperatures suitable for <br />growth, and to stimulate earlier spawning. How- <br />ever, such enhancement must becautiously consid- <br />ered because it might also benefit undesirable spe- <br />cies -perhaps to the ultimate detriment of Col- <br />orado squawfish. Water-development programs <br />that reduce available temperatures should of <br />course be avoided. <br />Investigations should be conducted to determine <br />the relation between the size of age-0 Colorado <br />squawfish and overwinter survival. If an important <br />relation occurs, it would provide useful objectives <br />for possible growth-enhancement efforts. <br />Because elimination of introduced fishes is im- <br />practicable in a river system as large as the Col- <br />orado, concern must clearly be directed toward <br />preventing introductions of additional, undesirable <br />fishes to the already large non-native fauna. In- <br />vestigations to determine which non-native fish <br />species present problems for Colorado squawfish <br />should be conducted. Perhaps ways can be found to <br />reduce the negative effects of the important non- <br />native fishes on the Colorado squawfish. <br />lxmx <br />%mxx <br />S F S F S F <br />0-26 1.0 1.0 0 0 0 0 0 0 <br />3 1.0 1.0 0 6.5 0 6.5 0 19.5 <br />4 1.0 1.0 0 6.5 0 6.5 0 26.0 <br />5 1.0 1.0 0 6.5 0 6.5 0 32.5 <br />6 1.0 1.0 0.5 6.5 0.5 6.5 3.0 39.0 <br />7 1.0 1.0 0.5 6.5 0.5 6.5 3.5 45.5 <br />8 1.0 1.0 0.5 6.5 0.5 6.5 4.0 52.0 <br />9 1.0 1.0 0.5 6.5 0.5 6.5 4.5 58.5 <br />10 1.0 1.0 0.5 6.5 0.5 6.5 5.0 65.0 <br />11 0.0 0.0 0 0 0 0 0 0 <br />Sums 2.5 52 20 338 <br />., <br /> <br /> <br />a For slow-growing population, G = (ElxmAx)/R° = 20!2.5 = 8 years; r = (IogeR°)/G = 0.916/8 = 0.115; and f = e' = 1.121. For <br />fast-growing population, G = 338/52 = 6.5 years; r = (Ioge52)/G = 0.608; and f = 1.837. <br />Values apply to ages 0, 1 and 2. <br />