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<br />66 <br /> <br />CIlAPTER 4 <br /> <br />STREAM ECOSYSTEMS <br /> <br />Introduct1cm <br /> <br />Historically, aquatic research has been concentrated on small streams <br />(first to fourth order) because of greater ease of sampling and a lesser <br />degree of man-caused perturbation. Although monitoring types of studies on <br />large streams have increased as a result of federal rE'quJ.rements for <br />environmental impact statements, basic research continues to be <br />concentrated on smaller streams. <br /> <br />As discussed in Chapter 3, stream ecosystems may be divided :lnto the <br />channeled aquatic zone and the riparian streambank zone. The two zones may <br />be studied individually or as a combined ecosystem. ,/hen studied as a <br />combined ecosystem it is viewed as containing one aquatic zone and two <br />adjacent riparian zones that are bordered by two upland terrestrial zones. <br />When studied separately, the aquatic zone may be restricted horizontally <br />between the opposite high water marks and lClngitudinally between the <br />headwaters and mouth or estuary. The upper and lower boundaries and length <br />of the linear segment of a stream ecosystem are usually arbitraril,y defined <br />by the investigators and the nature of the question bE,ing asked. Therefore <br />stream ecosystems may range from a short segment or re!Bch of one stream <br />order to the entire coalescing network of streams in a, drainage z)'stem that <br />forms a complex gradient of environmental variables and conditions <br />dominated by width, depth, velocity, flow volume, temperature and entropy <br />gain (Vannote et al. 1980). <br /> <br />BiOlogically, temperate zone streams are the result of hundreds of <br />1Ili11ions of years of evolution and at leas t 10 to 20 thousand years of <br />acclimatization and adaptation of resident populations (Cummins 1979). It <br />is already clear that with only minor exceptions, all streams fourth order <br />and larger within the 21 maj or drainage basins of the United States <br />(excluding Hawaii and Alaska) have been significantly impounded with dams <br />and reservoirs, channelized, polluted, overgrazed, de"atered, etc. The <br />tragic result of man-caused perturbations on the limited remaining milage <br />of large streams is that we may never know how streams function <br />biologically (Cummins 1979). <br /> <br />The whole subject of streams as ecosystems has been reviewed and <br />discussed in recent years in a number of excellent volumes including: The <br />Ecology of Running Waters by H.B.N. Hynes (1970), River Ecology and Man by <br />Oglesby, Carlson and McCann (Eds.) (1972), Fiver Ecolo~ by B.A. Whitton <br />(Ed.) (1975), Fundamentals of Aquatic Systems by R.S.K. Barnes and K.H. <br />Mann (Ed.) (1978), Perspectives in Running Water Ecolo~ by M.A. Lock and <br />D. Williams (Eds.) (1981), and Dynamics of ~otic Ecosystems by T.D. <br />Fontaine and S.M. Bartell (Eds.) (1983). They are recommended for a more <br />comprehensive treatment than is possible here. The following represents a <br />