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Chadwick and Associates, 1986; Hermann and others, <br />1986; Rader and Ward, 1987x, b; Evans, 1988; Bergey <br />and Ward, 1989; Wu, 1989; Kondratieff and others, <br />1990; Marmonier and Ward, 1990; Ruiter, 1990; <br />Lehnertz, 1991; Ruby and others, 1991; Ward and <br />Kondratieff, 1992; McCafferty and others, 1993). <br />Six studies were on the effect of reservoirs on inverte- <br />brates (Ward, 1974, 1976, 1987; Gray and Ward, 1982; <br />Cline and Ward, 1984; Zimmerman and Ward, 1984). <br />Four studies reported invertebrate distributions <br />along an altitudinal gradient (Ward and Berner, 1980; <br />Ward, 1981, 1982, 1986). Three studies reported on <br />invertebrate communities in relation to water quality <br />(U.S. Environmental Protection Agency, 1972; <br />Woodling, 1977; Deacon and Vaught, 1993). One <br />study reported on the long -term trends in the macroin- <br />vertebrate communities in the Cache la Poudre River <br />(N.H. Voelz, J.V. Ward, and K.L. Martin, written <br />commun., 1993). One study reported on the relation of <br />discharge fluctuation on invertebrate communities <br />(Canton and others, 1984), and one study reported <br />on the effect of highway construction on invertebrates <br />(Cline and others, 1982). There is abundant informa- <br />tion about the invertebrate communities in the moun- <br />tain region and limited information about invertebrate <br />communities in the plains region. <br />Fish Communities <br />Fish community studies were the most wide- <br />spread throughout the South Platte River Basin <br />(table 1). There were only 7 studies published from <br />1891 to 1950 on fish communities, and the remaining <br />36 studies were published after 1950. Of the 43 inves- <br />tigations concerning fish, 13 examined sites in moun- <br />tains and in plains, 12 examined sites only in the <br />mountains, 1 examined sites in the mountains and tran- <br />sition zone, 4 examined sites only in the transition <br />zone, 2 examined sites in the transition zone and plains, <br />and 11 examined sites only in the plains. The types of <br />fish investigations included 12 studies on sport fisher- <br />ies management (Hepworth, 1973; Marshall, 1973; <br />Goettl, 1980, 1981, 1982; Wiltzius, 1981; Culver and <br />Bestgen, 1983, 1986; Anderson and Nehring, 1985; <br />Rosenlund and Stevens, 1988, 1990; Stevens and <br />Rosenlund, 1990). Six studies were on fish identifica- <br />tion or a historical perspective (Jordan, 1891; Juday, <br />1904, 1905; Cockerell, 1908; Ellis, 1914; Beckman, <br />1952). Ten studies described fish distribution on a sub - <br />basin or basin scale (Johnson, 1942; Li, 1968; Baxter <br />and Simon, 1970; Propst, 1982; Bestgen and Culver, <br />1985; Woodling, 1985; Chadwick & Associates, Inc., <br />1986; Propst and Carlson, 1986; Chart and others, <br />1987; Lehnertz, 1991). Similarly, two studies describe <br />the status and trends of the fish communities at four <br />sites in the Big Thompson River, near Loveland, <br />Colorado (K.R. Bestgen and K.D. Fausch, written <br />commun., 1993a), and at 10 sites in the Cache la <br />Poudre River, from Fort Collins to Greeley, Colorado <br />(K.R. Bestgen and K.D. Fausch, written commun., <br />1993b). Four studies reported information on single <br />species of fish (Andrews, 1970; Platania and others, <br />1986; Bestgen, 1989; Propst and Carlson, 1989), and <br />two studies described the fish community in relation to <br />water quality (Woodling, 1977; Lewis and Saunders, <br />1985). Three studies described fish distribution on a <br />local scale (Hendricks, 1950; Boaze, 1977a, b), one <br />study related discharge to fish communities (Canton <br />and others, 1984), one study described food habits of <br />fish (Eder and Carlson, 1977), one study described the <br />fish communities in irrigation ditches ( Platania, 1990), <br />and one study described the development of an index of <br />biotic integrity for fish communities in the South Platte <br />River Basin (Schrader, 1989). <br />Habitat Characterization <br />Of the 14 studies conducted measuring habitat <br />characteristics, 13 studies were in the plains, and only <br />1 study was in the mountains. In the Great Plains <br />province, eight studies described flood -plain vegeta- <br />tion (Christy, 1972a, b; Jackson, 1972; Jackson and <br />Lindauer, 1978; Lindauer, 1983; Sedgwick and Knopf, <br />1989; Snyder and Miller, 1991; Johnson, 1994), and <br />five studies discussed flood -plain vegetation in relation <br />to flow regime or geomorphology (Williams, 1978; <br />Crouch, 1979; Eschner and others, 1983; Knopf and <br />Scott, 1990; Friedman, 1993). The study of flood -plain <br />vegetation in the mountains (Reid and Bock, 1978) <br />only described results of multivariate analyses and did <br />not describe the types of vegetative community. As a <br />result, there is an information gap for habitat character- <br />istics in the mountains and the transition zone. <br />Chemicals in Organism Tissue <br />There have been only five studies on chemical <br />contamination in fish tissue conducted in the South <br />Platte River Basin, and all the studies had sites that <br />were located in the plains. Two studies reported only <br />organochlorine contaminants in fish tissue (Schmitt <br />and others, 1990; U.S. Environmental Protection <br />Agency, 1992), and two studies reported only trace <br />elements in fish tissue (Walsh and others, 1977; <br />Lowe and others, 1985). DeWeese and others (1993) <br />measured organochlorines and trace elements in fish, <br />crayfish, filamentous algae, and sediments. There is a <br />basinwide gap in information on chemicals in organism <br />tissue. <br />INVENTORY OF BIOLOGICAL INVESTIGATIONS <br />