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<br />1581 <br /> <br />warm wa<er fish population is be" supported by a <br />full reservoir rhrough July 15, followed by a rapid <br />draw down between July 15 and August 15, The <br />rapid drawdown allows colonizarion of the <br />exposed substrate by annual species during the <br />growing season, which contributes to reservoir <br />food supplies when reservoir levds rise again. <br />Given these conflicting demands, the overall <br />reSOurce preference is to prevent draw down as <br />long as possible in rhe spring, within the confines <br />of opera<ional demands. <br /> <br />B. Summary of Natural Resource <br />Water Preferences by Individual <br />Resource Values <br /> <br />I. Water Preferences for Fish Populations <br /> <br />a. Arkansas River <br />The Arkansas River is no red for its exceprional <br />brown trout fishery and for its devdoping rain- <br />bow rrout fishery. Brown rrour were rhe focus of <br />rhis smdy because of rheir prevalence in the river, <br />because the popularion is sdf-sustaining, and <br />because my given operational program will influ- <br />ence rainbow trour in a similar manner. There are <br />a nllmb~r of non-game fish species present in me <br />Arkansas River drainage, primarily found between <br />Canon Ciry and Pueblo Reservoir. This area was <br />nor exrensivdy studied, but flows rhar protect and <br />mainrain game species should also protect non- <br />game species. Rare species, such as greenback cur- <br />rhroar trour, Arkansas River darter, and redbeIly <br />dace, are all found in the upper Arkansas River <br />basin bur have nor been collected in rhe main- <br />stem river or reservoirs. Habitat needs for brown <br />trout and rainbow rroU[ were analyzed using the <br />lnme:un Flow Incremenral :Vlethodology (IFIM). <br /> <br />The twO mo" importanr physical variables affect- <br />ing fish habirat on the Arkansas River are vdociry <br />and depth. The further these variables are from <br />rhe optimum value, the less likdy thar position is <br />going [Q be occupied by a rrout. because brown <br />[roU[ occupy positions in a stream that maximize <br />net energy gain during foraging. The c:lIrying <br />capaciry of a meam may be determined by avail- <br />able habirar and number of foraging sites. <br /> <br />Increosing flows frequenrly produce unfavorable <br />habitat condirions in rhe Arkansas River, as ill us- <br />crated in Appendix X. <br /> <br />Increasing vdociry accounts for large drops in <br />suitable habirat, particularly for small tlsh. For <br />example, adulr brown erout prefer a vdociry of <br />1.3 feer per second for spawning, and vdocities <br />ranging from 0.9 co 1.3 per second for orher <br />activities, such as foraging. However, fry and juve- <br />niles prefer vdociries of 0.3 [Q 0.7 teet per second. <br />For all life "ages, increased vdocir;es nor only <br />increase the merabolic cOst associared wirh forag- <br />ing, but also create conditions chat reduce the <br />capmre of drifting insecrs. <br /> <br />As with velocity, increasing depth accounts for <br />drops in suirable habirar, especially for small fish. <br />Depths of 2.0 to 3.0 feer are oprimum for aduIr <br />brown erour spawning, while the suirable range of <br />deprh for spawning is 4.8 co 36.0 inches. Redds <br />a<e generally found ar deprhs of 12.0 to 36.0 <br />inches. However, juvenile brown troUt have opti- <br />mum habirar depths ranging trom 0.9 co 1.7 feer. <br />Finally, because brown crout are boaom-oriented, <br />visual feeders, greater depth cre:lCes conditions <br />thar reduce the captUre of drifting insects. <br /> <br />In coldwater environments, troue growth is a <br />good indicacor of the health of an aquaric ecosys- <br />tem because it integrates all the biotic and abioric <br />variables impacting organisms and reflecrs sec- <br />ondary effecrs of chronic seress. Pre- and pOS!' <br />runoff periods (April-May and July-Seprember) <br />are critical for brown <rOut gtowth and survival, <br />because there is a strong correlation between <br />brown rrour growth and discharge in rhe Arkansas <br />River. Warmer water temperamres and poor prey <br />availabiliry make AuguS! and September particu' <br />larly critical months for rroU[ growth. The nega- <br />rive impacts trom higher flows are not offset by <br />releases of cooler warer from Twin lakes in <br />August and September, because rhese releases will <br />not decrease Water temper:uure for my J.pprecia~ <br />ble dist:U1ce downsrre:un. <br /> <br />To oprimize the amounr of available brown erouc <br />and rainbow trOUt habirar for all life stages on the <br />Arkansas River from near leadville co Pueblo <br /> <br />29 <br />