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<br />. ..0 -- ..' - <br /> <br />-:,_.... <br /> <br />-.~ <br /> <br /> <br />'. <br />._0_--0-:-: <br /> <br />"-.__"0:_.:'-; .__.0_":-:-- <br /> <br />o . . .. <br />-.... ... . . <br /> <br />-. .- <br />,. -' -.. --' <br /> <br />....- _.~ " <br /> <br />.' <br />:. . <br /> <br />o . '. ._: _.. _. <br />. :.. ...~. -.:: -~,: ..' <br /> <br />;~r;;{;<' <br /> <br />..";"........ "---..;,.- <br /> <br />178 <br /> <br />D. J. ORTH <br /> <br />instream flow-habitat model. The following suggestions are offered for future instream flow assessments <br />and research: <br /> <br />1. Microhabitat availability is not the only factor limiting fish populations and does not operate <br />continuously. Therefore, persons using IFIM must identify the time(s) when microhabitat is most <br />critically limited and avoid the mistake of assuming that WUA is positively related to fish abundance <br />at all levels of WUA at all times. <br />2. Because food availability may limit abundance, habitat suitability criteria for invertebrates must be <br />developed and used in PHABSIM applications. New approaches for assessing instream flow needs for <br />invertebrate production must be developed and tested. <br />3. Habitat suitability criteria can vary with body size, season, time of day, activity, predators, and <br />competitors. Therefore, the applicability of habitat suitability criteria is limited to sites with similar fish <br />assemblages and thermal regimes. Furthermore, seasonal (or size-related) differences in habitat needs <br />and limiting factors must be identified and incorporated in assessments. <br />4. Structural complexity plays a major role in position choice by stream fishes through the need to feed <br />efficiently and avoid predators. Greater emphasis must be placed on developing reliable criteria for <br />defining suitable habitat for fishes and invertebrates. <br />5. Assessments must address the needs of a wider array of target species, especially non-game fishes and <br />invertebrates in order to recommend flows to maintain ecological integrity of steam ecosystems. <br />6. Temperature and water quality limitations on fish and invertebrate populations are potentially severe <br />and should be evaluated in instream flow assessments. <br /> <br />Although the need for more research is obvious and the complicating factors which I have discussed <br />may seem to make the problem intractable, the benefits of improved stream management are undeniable. <br />In the near future, assessments can be greatly improved by applyin.,g.o.I,l,!:Q!'esent knowledge of stream fish <br />ecology. The IFIM is not intended to be a panacea~owever, IFIMhas.the potential to identify limiting <br />habitat events and avoid them in developing flow regimes in regulated rivers._l'he IFIM is a process, not a <br />model, and the process allows the consideration of the other ecological factors that I have discussed. As <br />new models are developed and tested they can be incorporated into ~he IFIM process. However, it is still <br />not possible, with our current knowledge base, to accurately predicHish population sizes under various <br />flow regulation scenarios - this remains as a goal fer:research. The additional cost for studying all the <br />factors that I have discussed may not be feasible for all agencies to consider, ex~ept in a research mode; <br />the pressure to take short cuts in assessments will continue. More detailed, cOmprehensive studies of <br />stream fish and invertebrate responses to altered flow_ regimes will be needed before simpler and less <br />costly methods evolve. In the meantime, flow recommendations developed on the basis of incomplete <br />assessments should, by necessity, be overly conservative to protect stream resources. <br /> <br />ACKNOWLEDGMENTS <br /> <br />1-. <br /> <br />I thank P. L. Angermeier, C. J. Goudreau, P. M. Leonar~l,~a;d M. D. Lobb for their reviews and <br />discussions of this paper. Two anonymous reviewers also made important suggestions for this paper. <br /> <br />REFERENCES <br /> <br />Allan, J. D. 1982. 'The effects of reduction in trout density on the invertebrate community of a mountain stream', Ecology, 63, <br />1444-1455. . '0"-" ';' ...,' . <br />Angermeier, P. L. 1985. 'Spatio-temporal patterns. of foraging success f~r. ~shes in, an Illinois stream', Am. Midl. Not.., 114, <br />'342"';359. .' .'.'..___, ,.- '_.', '. ': , <br />Angermeier, P. L. and Karr, J. R. 1984. 'Relatio~shipsbetween woody debris 'and fish habitat in a small warm water str.earn', Trans. <br />:;Am:FiI'h.Soc., 113,716-726.'1::::"": ~." .; ") ..,... ".J ,:..,;J....,.;..~ ;,":i F) ~.::.,:...::, ... .-'.:.." '. ... -."."--< <br /> <br />'AnderSon, C. S. 1985. 'The structure of sculpin populations along a stream size gradient', Environ. Bioi. FiI'h.;13, 93-102. ~';b- . <br />