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<br />in the FPB came by way of the river; 11,374 were <br />caught in the river trap (Table 1). After two extraor- <br />dinarily wet years, river access was no longer <br />impeded by the Truckee River Delta, and cui-ui <br />abandoned the use of the fishway. <br /> <br />Upstream Migration <br /> <br />Cui-ui on their spawning migration up the fish- <br />way and into the FPB were collected, counted, <br />sexed, measured (fork length), and checked for tags. <br />The fish were then either released into a backwater <br />area directly above the dam or trucked farther <br />upstream and released into the main stem of the <br />Truckee River. <br />In 1982-84 the cui-ui migration began as early as <br />9 April (in 1984) and ended as late as 21 June (in <br />1982), The three migratory runs lasted 48 to 59 <br />days, while water temperatures ranged from 9 to <br />20oC; however, migration peaked :2: 500 fish per <br />day) when water temperatures ranged from 9 to <br />170C and daily means were 12 to 150C (Fig. 4). Sub- <br />jective observation indicated that upstream migra- <br />tion was generally stimulated by rising temperatures <br />and dampened by falling temperatures, These <br />responses to temperature seemed to be both sea- <br />sonal and diurnal; over a 24-h period the cui-ui run <br />was heaviest in late afternoon and evening, when <br /> <br />7 <br /> <br />temperatures were highest. This relation between <br />water temperature and the spawning migration of <br />catostomids in general has been observed by others <br />(Bailey 1969; Corbett and Powles 1983; Geen et al. <br />1966) . <br />To enable us to follow migrating adult cui-ui in <br />the river and locate spawning areas, we applied <br />external radio-tags to 57 fish captured at the FPB-8 <br />in 1982, 27 in 1983, and 23 in 1984 (totals exclude <br />1 fish bearing a transmitter that failed to operate). <br />A stainless steel wire was routed through the base <br />of the pterygiophores and each end was fastened <br />to a plastic harness trailing behind the dorsal fin. <br />Radio-tags were of three sizes; the largest was <br />60 mm long and 12 mm wide and weighed 20 g. <br />Transmission life was 30 to 60 days. A Smith-Root <br />RF-4 receiver was used to track fish in the field, and <br />a Smith-Root Field Data Logger (FDL-lOER) was set <br />at the FPB to record the date and time when tagged <br />fish dropped over MB dam as they returned to <br />Pyramid Lake. <br />Of the 57 fish tagged (28 males and 29 females), <br />12-most of which had been tagged late in the <br />run-returned to the lower river over MB dam <br />within a few hours after their release. The rest <br />remained in the stream for 4 days or longer. <br />The radio-tagged cui-ui migrated only short <br />distances after they were released above the dam, <br />After being tagged at the FPB (after they had moved <br /> <br />Table 1, Numbers of cui-ui entering the fish processing building (FPB) through the Pyramid Lake <br />fishway and the river trap, 1976-1984. <br /> <br /> Identifying Total flows <br /> Number entering FPB numbers of March through May <br /> Through Through ladders in Truckee River <br />Year fishway river modified a (hectare-meters) <br />1976 0 0 None 9,565 <br />1977 0 0 None 1,172 <br />1978 33 0 1 2,470 <br />1979 139 0 1 4,830 <br />1980 4,984 0 1, 2 19,405 <br />1981 47 0 1-4 9,018 <br />1982 13,804 1 1-4 59,283 <br />1983 5,994 20 1-4 83,653 <br />1984 0 11,374 1-4 32,983 <br /> <br />a See Fig. 1 for location ofladders. In ladder I, velocity was reduced in 1978 and turbulence in 1979. Similar modifications were <br />made in ladder 2 in 1980 and in ladders 3 and 4 in 1981. <br />