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1994 & 1995 GUNNISON RIVER RZ RADIOTELEMETRY <br />DISPLACEMENT <br />.112 <br />.130 <br />N .170 <br />.320 <br />.380 <br />.390 <br />i .400 <br />' .410 <br />.440 <br />.? .460 <br />} .470 <br />V .480 <br />Z .502 <br />W .520 <br />.560 <br />Q .600 <br />W .640 <br />.660 <br />U. .680 <br />O .700 <br />.740 <br />Q .760 <br />Q .780 <br />.800 <br />.820 <br />UPSTREAM <br />DOWNSTREAM <br />n=23 <br />1994: April-August <br />1995: March-October <br />Data <br />20 15 10 5 O 20 40 60 80 <br />RIVER MILES <br />Figure 6. Total maximum upstream and downstream displacement (from <br />release point: '0' on the X-axis) for 25 radiotagged adult <br />razorback sucker monitored between March and September 1994 <br />and March and September 1995 in the Gunnison River, Colorado. <br />Note: the upstream scale is one-fourth that of the downstream <br />scale. <br />At the end of the study, 3 fish were confirmed alive, 3 were missing, 2 <br />were confirmed dead, and 17 were presumed dead. Nine radiotags were recovered, <br />the first on 5 May, the last on 23 August 1994. As with fish stocked in the <br />Upper Colorado River, mortality of razorback sucker stocked in the Gunnison River <br />in 1994 did not appear to be immediate but delayed following release. Post- <br />stocking survival was low for fish stocked in the Gunnison River during 1994 and <br />1995: confi rmed mortal i ty was 8%; actual mortal i ty mi ght have been as hi gh as 88% <br />if missing and presumed dead fish were included. <br />San Juan River <br />One concern when stocking fish in large rivers is the vast downstream <br />displacement that usually follows release. Movement data from pond-reared <br />razorback sucker released in the Upper Colorado and Gunnison rivers indicates <br />that the majority of downstream displacement occurs within the first few weeks <br />14