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<br /> <br /> <br />-;:~ <br />,'~ <br /> <br />The recaptures of 30 razorback sucker, of which three were recaptured twice, have <br />aided in understanding their distribution and spawning behavior. A total of <br />16 fish were local recaptures, tagged and recaptured within about one <br />month's time (11 in 1984 and 5 in 1981). With some exceptions, these <br />fish remained near the original capture locations. An additional 14 recaptures <br />were recovered after a year or more and included recaptures of up to 6 years <br />duration (lable 2). The distances moved by these fish over the years ranged <br />from 0 to 129 miles. The data were then partitioned to separate recaptures <br />within three time periods: breeding, nonbreeding, and combination breeding and <br />nonbreeding periods. This was accomplished by segregating May and June as <br />breeding months. Fish tagged and recaptured during the breeding season (9) <br />averaged only 7 miles movement and one fish tagged and recaptured during the <br />nonbreeding season travelled only about 1 mile. However, 5 fish tagged in <br />the nonbreeding and recaptured in the breeding season (or vice versa) averaged <br />51.4 miles distance between captures. The preceding indicates that the <br />razorback is sedentary during most of the year, perhaps making only local <br />movements, but may travel longer distances to reach suitable spawning grounds. <br />These local movements are demonstrated by one razorback sucker implanted with <br />a radiotransmitter in 1980 (Tyus, et al. 1981). This fish moved about 3.8 miles <br />downstream of its capture location and into the Duchesne River. It remained <br />less than 1 mile inside the Duchesne River until flooding occurred in early <br />June when it moved into the Green at the mixing zone of the two rivers and was <br />lost and presumably spawned at some unknown location. The sucker then was <br />relocated in July near the same area and slowly moved upstream in the Green <br />River about 7 miles, when contact was lost August 13. <br /> <br />~, <br />'-t: <br />'.~ <br /> <br />';i <br />; <br /> <br />HABITAT USE <br /> <br />Microhabitats and specific physical conditions required by the razorback <br />for spawning are still somewhat of a mystery and the fish appear to stage <br />and spawn in different habitats. A large concentration of razorbacks discovered > <br />by Vernal Dialogists in 1981 at the junction of the Green River and Ashley <br />Creek (Tyus et al. 1982) prompted many collecting trips up Ashley Creek in <br />search of spawning areas. 10 date, none have been discovered in Ashley Creek <br />and no razorback has been captured further upstream in the creek than 0.3 <br />miles, habitat that does not appear suitable for spawning because of the <br />silty substrate. It is possible that the large shallow eddy produced at this <br />location makes it desirable for a staging area. Fish tagged early in May at <br />the mouth of Ashley Creek and recaptured further upstream in the Green River <br />in ripe spawning condition tend to support this hypothesis. Most ripe <br />razorbacks were collected over coarse sand substrate; however, some were <br />collected near gravel and cobble bars. Temperatures at the point of capture <br />for the ripe fish ranged from 10.5 C (May 10) to 18 C (June 14) in the Green <br />River during 1984 collections, averaging about 15 C. The USGS records for <br />Jensen indicate that the river flow during this time period varied from <br />13,800 to 38,500 cfs, and averaged 26,100 cfs. The river peaked on May 18, <br /> <br />":i- <br /> <br />..'~ <br /> <br />',' <br />, <br />.. <br />, <br /> <br />:.1 <br />. <br />.' <br /> <br />.t~ <br />2 <br /> <br />- <br />.>. <br />-~ <br /> <br />'.~ <br /> <br />'* <br />, ..fl <br />) <br /> <br />198 <br /> <br />