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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
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