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<br />280 <br /> <br /> <br />FISH CULTURE IN FISHERIES MANAGEMENT <br /> <br />areas extended from the river-lake interface to <br />the city of Wadsworth, 30 miles up stream. This <br />area is not now accessible for spawning because <br />of dam construction. In addition, during drought <br />and ensuing low-flow years, cui-uis cannot traverse <br />tile large delta that be~omes a barrier because of <br />the gradual drop in lake level. An additional <br />barrier occurs 2.98 miles up stream at the Marble <br />Bluff Dam and Fishway. The fishway is used by <br />cui-uis, but passage around the dam is not presently <br />possible. Further, suitability of the river above <br />the dam is marginal for natural propagation be- <br />cause of poor water quality and minimal spawning <br />substrate. <br /> <br />Program Effectiveness <br /> <br />A gill-netting program was conducted at Pyr- <br />amid Lake from 1956 to 1958 by the Nevada <br />Department of Fish and Game (Johnson 1958). <br />A similar program was carried out between 1975 <br />and 1977 by a private consulting firm (Sigler and <br />Kennedy 1978). Results were as follows during <br />the two respective periods: <br /> <br /> 1954- Nov. 1975- <br />Cui-ui catch statistics 1958 Dec. 1977 <br />Number of net sets 133 373 <br />Number of cui-ui 307 415 <br />Number of cui-ui <br />per net 2.31 1.11 <br />Percent of total 4.40 1.28 <br /> <br />The decrease in the cui-ui component of the total <br />catch (Sigler and Kennedy 1978) reinforces the <br />concern that the cui-ui may have declined in <br />numbers during this 20-year period. Although <br />netting techniques may have differed between <br />studies, catch-per-unit-effort was reduced by half. <br />Impact of the cui-ui hatchery on recovery of <br />the species may never be known. Dramatic prog- <br />ress of the hatchery propagation program has <br />occurred. as evidenced by the enormous success <br />of the 1982 operation. Development of rearing <br />techniques is the predominant reason for success <br />of this program. Techniques that have been de- <br />veloped and refined came only from intimate <br />, knowledge gained by hatchery personnel involved <br />in observations of the fish and the operating <br />system. Mastery of the art of cui-ui rearing comes <br />from many inputs, too subtle to define and ob- <br />tainable only by gaining "hands-on" experience.. <br />Success in terms of benefit to the resource is more <br />tenuous, but the hatchery program does insure a <br /> <br />steady recruitment of healthy larval fish into ;Pyr- <br />amid Lake. Future research shouh;l include, (1) <br />methods for rearing large numbers of cui-ui to <br />fingerling size, (2) evaluation of survival of planted <br />cui-uis, and (3) monitoring the cui-ui population <br />for age-composition changes. j' <br /> <br />; ~,~., -i'; ~ <br /> <br />Culturing an Arizona Native . Trout " <br />. 'It . 'i . <br />In the early 196Os, personnel of the AG&F <br />Department's Fisheries Branch recognized the <br />then undescribed Apache trout (Salmo apache) <br />as a unique salmonid that was declining in relative <br />abundance and occurrence (U .S. Dept. of In,terior <br />1983). In 1963j a total of 82 Apache trout were <br />collected from Ord Creek on the headwaters of <br />the White River, Apache County, Arizona. They <br />were transferred to the Department's Sterling <br />Springs Hatchery, located on the Coconino Na- <br />tional Forest on the headwaters of Oak Creek. <br />Spring flow is 31.1 ft3/min, with an average tem- <br />perature of 510F. Seasonal temperature fluctua- <br />tions are never more than 2.0oF. This initial brood <br />stock and subsequent generations served as the <br />gene pool for the Apache trout rearing program <br />in 1974. .... . ' <br />With enactment of the ESA, the Apache trout <br />was listed as an endangered species. Because of <br />misunderstandings and misinterpretations of the <br />nature of the protective status afforded' an' en- <br />dangered species, the Apache trout ~earing pro- <br />gram became jeopardized. Local press coverage <br />claimed that many of Arizona's trout waters would <br />be closed to angling because they had been stocked <br />with Apache trout. I~ was not long afterward when <br />all Apache trout in capt;vi~y mysteriously disap- <br />peared. In 1975, the Apache trout was down- <br />listed to threatened status, and 118 individuals <br />were collected from Soldier Creek, Apache!Cciunty, <br />Arizona, on the headwaters of the Black River. <br />Subsequent offspring from these fisl\'constitutes <br />the brood stock for the present rearing program. <br /> <br />Culture Results <br /> <br />Standard fish-culture procedures were used' in <br />rearing Apache trout (Leitritz and Lewis 1980). <br />Eighteen years of intensive culture data indicate <br />that Apache trout may not spawn anQually. Two- <br />year-old male spawners have good milt production, <br />but production is greatly reduced in 3- and 4-year- . <br />. olds, and yield is approximately 1 ml pe{stripping. <br />. Two-year-old females produce few eggs, and older <br />'I ,,~ <br />females may not produce eggseverysea59 <br />';,;.'-~,':W0t~ - <br /> <br /> <br /> <br />1 ; , ~ <br /> <br /> <br />:;',,-"'- <br />