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7/14/2009 5:02:30 PM
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UCREFRP
UCREFRP Catalog Number
7405
Author
Bain, M. B., ed. 1990.
Title
Workshop Synopsis,
USFW Year
Ecolog
USFW - Doc Type
U.S. Department of the Interior,
Copyright Material
NO
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<br />16 BIOLOGICAL REPORT 90(5) <br /> <br />Fish Community Structure and Stability <br />in Warmwater Midwestern Streams <br /> <br />by <br /> <br />William J. Matthews <br /> <br />University of Oklahoma <br />Biological Station <br />Kingston, Oklahoma 73439 <br /> <br />Impact assessment generally implies a search for <br />ways to measure and predict changes in stream <br />systems that ensue from cultural alterations. In <br />order to really know the degree to which a cultural <br />activity results in change in stream systems, some- <br />thing must be known~of the magnitude of change <br />or variation that occurs naturally. Even if managers <br />are constrained from long-term studies of each <br />stream of interest, the long-term data sets that do <br />exist can be used to predict the kinds and degree <br />of changes that may naturally occur in a variety of <br />stream systems. <br />Over the last two decades, a relatively long-term <br />data base has been accumulated from our collecting <br />activities assessing fish assemblages and faunas in <br />three midwestern streams: Piney Creek, Izard <br />County, Arkansas; Brier Creek, Marshall County, <br />Oklahoma; and Kiamichi River, southeastern Okla- <br />homa (Ross et al. 1985; Matthews 1986; Matthews <br />et al. 1988). These data sets have been evaluated <br />at two levels: stability of whole-stream faunas <br />(based on pooled collection data at multiple sites <br />on each stream) and stability of fish assemblages <br />at each individual site over time. The data set spans <br />1969-86 for Brier Creek, 1972-86 for Piney Creek, <br />and 1981-86 for Kiamichi River. Each of these time <br />intervals allows for one to two complete generations <br />of at least the small fish species that are most <br />abundant. <br />The whole-stream faunas of all three streams have <br />been highly persistent (in terms of presence and <br />absence of species) and stable (based on abundance <br />data) in all years of study. No common species has <br />been lost from any of the streams, and no "rare" <br />species has become common at any of the sites. Both <br />similarity indices (Morisita's and percent similarity) <br />and statistical rank correlation of species abun- <br />dances show that all three streams have been stable, <br />and that the most environmentally stable stream <br />(Piney Creek of the Ozark uplands) has had the <br /> <br />greatest degree of fish population stability across <br />all years. <br />At individual sites on each of the streams, the local <br />fish assemblage has had a tendency to be stable, <br />although exceptions exist in all three systems. <br />Where individual collecting sites have shown a <br />marked change in the composition of the fish assem- <br />blage, this change can usually be attributed to known <br />events, such as deposition of large woody debris by <br />floods, death offish in intermittent headwaters due <br />to drought, or other such disturbances. However, <br />recolonization of intermittent headwaters is not a <br />random phenomenon. Matthews (1987) showed that <br />existence and persistence of fish species in harsh <br />headwaters of at least one of the streams was <br />directly related to their ability to withstand low <br />oxygen conditions, which are common. Thus, there <br />is both a chance component and a directed compo- <br />nent to dynamics of assemblage composition in head- <br />water streams. <br />The long-term study of Piney Creek included a <br />flood event that was clearly of 100-year magnitude. <br />Vertical water levels were elevated as much as 12 m <br />at some sites, and physical destruction and distur- <br />bance of habitat along the creek was extreme. Im- <br />mediately after the flood, fish assemblages showed <br />some differences from those that existed before the <br />flood, but after 8 months, both the whole-stream <br />fauna and most local assemblages were statistically <br />indistinguishable from their composition before the <br />flood. This well-documented event-and other ac- <br />counts of flood effects on fish in midwestern streams <br />(Gelwick 1990; Harvey 1987)-indicates that while <br />floods may have an immediate effect on composition <br />of midwestern fish communities, these changes are <br />largely transient, with the systems returning to <br />preflood conditions rather rapidly. <br />Some methodological recommendations are pos- <br />sible from collections made on these streams. There <br />is a longstanding question in fish community assess- <br /> <br />~ <br />
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