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<br />474 <br /> <br />EMLEN ET AL. <br /> <br />existing adults can be calculated from the esti- <br />mated (adjusted Peterson method) 1983 adult <br />population of 146,000 and the contributions of <br />larvae from year-classes 1976-1980 (correspond- <br />ing to adults entering the population between 1984 <br />and 1988). Using larvae estimates provided in Bu- <br />chanan and Strekal (1988) this becomes <br /> <br />(146,000)(0.85)7 <br />+ (33,000 + 747,000)(0.001)(0.75) <br />x (0.444)(0.85)6 <br />+ (1,835,000)(0.00 I )(0. 7 5)(0.444)(0.85)5 <br />+ (57,000 + 5,663,000)(0.001){0.75) <br />x (0.444)(0.85)4 <br />+ (87,000 + 1,000)(0.001)(0.75)(0.444)(0.85)3 <br />+ (1,507,000 + 317,000)(0.001)(0.75) <br />x (0.444)(0.85)2 <br />= 48,144. <br /> <br />Based on a larval survival rate of 0.001, then, the <br />projected 1990 adult population is 7,416 + 48,144 <br />= 55,560. This is short of the estimated value of <br />300,000 by a factor of5.4. Hence we must consider <br />0.00 I to be a minimal estimate oflarval survival. <br />Because the survival estimate of 0.00 I seemed <br />high in regards to general ecological considera- <br />tions, a revised value five times that seems incon- <br />ceivable. In addition, it is entirely possible that <br />either the 1983 or the 1990 adult population es- <br />timates could be in error. Accordingly, 0.003 was <br />chosen as a compromise upper limit on estimated <br />survival. On the presumption that the real value <br />should lie somewhere between the minimal and <br />maximal estimates, 0.002 was picked as the "best <br />guess" value. <br /> <br />Predictions of Population Size <br /> <br />If the level of Pyramid Lake were to exceed <br />3,848 feet above mean sea level, the elevation of <br />the Marble Bluff Dam spillway, water would in- <br /> <br />~ m@rnowrn 00 <br />MAY 41994 <br /> FWRS <br /> <br />undate the delta, thereby enhancing fish passage <br />to the dam and, once the spillway was topped, <br />hugely facilitating transport upstream of the dam. <br />To reflect the corresponding benefits, number of <br />spawners was permitted to double under this sce- <br />nano. <br />Density dependence acts, at least in part, via <br />limits on the number of potentially spawning fe- <br />males that can migrate through the restricted pas- <br />sages leading upriver. Based on observations of <br />migrating females and the nature of the fishway <br />and the Marble Bluff Fish Facility river trap through <br />which the fish must pass, the maximum possible <br />run was set at 100,000 females. Other density ef- <br />fects probably occur, but information is not avail- <br />able on their mode of action or their intensity. It <br />was necessary, therefore, to ignore other density <br />effects in the model and to consider model output <br />to err on the side of overestimation offemale num- <br />bers. <br />No information exists on year-to-year variabil- <br />ity in demographic parameters. This being so, and <br />inasmuch as existing variation is almost certainly <br />not independent of hydrological events, it seemed <br />foolhardy and almost certainly misleading to mod- <br />el birth and death as stochastic processes. Quali- <br />tatively, fecundity and (probably) survival vary <br />positively with water flow. Therefore, as the vari- <br />ance in these parameters increases, the severity of <br />drought effects is magnified and population growth <br />is curtailed. By utilizing fixed values, the model <br />again errs on the side of overestimating numbers. <br />A population of two individuals cannot repro- <br />duce, even under ideal conditions, ifboth fish are <br />of the same sex. Under such circumstances, and <br />occasionally under even less stringent conditions, <br />a real population would die out. The model, by <br />ignoring this sort of statistical variation in fecun- <br />dity, ignores also the corresponding possibility for <br />extinction. In principle, this, yet again, means the <br />model might err on the optimistic side. In fact, <br />however, very few of the simulated populations, <br />even under conditions of no supplemental water, <br />ever fell below about 50 individuals without even- <br />tually going, and being recorded as, extinct. <br /> <br />