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<br />the middle Stillwater Canyon reach, 76 from the San Rafael River confluence reach, and 1 larva <br />was caught in the Green River Valley reach. <br />Capture dates of razorback sucker larvae over all years ranged from 16 May to 21 July in <br />the middle Green River and from 7 May to 9 July in the lower Green River. In most years, larvae <br />were first collected 20-30 d after the earliest estimated date of spawning and were usually most <br />abundant in samples collected before mid-June. Earlier first occurrence of larvae in collections <br />from the San Rafael River confluence or middle Stillwater Canyon reaches compared to <br />collections from the middle Green River suggested that razorback suckers reproduced in the <br />lower Green River each year during 1994-1996. <br />Estimated initiation of spawning by razorback suckers in each year during 1993-1996 <br />was generally associated with the beginning of spring-runoff flows and was probably triggered by <br />a suite of interacting environmental cues that could not be detected by analysis of single water <br />temperature and discharge parameters. Duration of spawning in either the middle or lower Green <br />River varied among years but usually spanned 4-6 weeks each year. Spawning occurred during <br />increasing and highest spring flows and encompassed a wide range of mainstem mean daily <br />discharges (78-696 m3 Is) and instantaneous daily water temperatures (8-21 OC). <br />Most larval razorback suckers (11-18 mm total length, TL) contained food items, and <br />mean percent fullness of digestive tracts increased with fish length (ranged from 35 to 65%). <br />Principal dietary components were chironomid larvae, cladocerans, rotifers, algae, and <br />miscellaneous debris. Estimated mean daily growth of razorback sucker larvae less than <br />35 d old collected from either river section during 1993-1996 was lowest in 1994 (0,31 and 0.27 <br />mm TL/d for the middle and lower Green River, respectively) and greatest in 1996 (0.35 and <br />0.33 mm TL/d). Over all years, specimens from the middle Green River grew 6-21 % faster than <br />those from the lower Green River. Although food abundance appeared adequate to meet the <br />minimum nutritional requirements for larval survival, the growth potential of razorback sucker <br />larvae is greater than we observed. Poor growth can significantly reduce the survival of fish <br />early life stages if size-dependent processes regulate year-class success. Extremely low survival <br />was suggested by the apparent disappearance of larval razorback suckers from Green River <br />nursery habitats by early or mid-July each year. <br /> <br />Vlll <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />r <br />I J <br />