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Floodplain Documents
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Statewide
Basin
Statewide
Title
Overview of River-Floodplain Ecology in the Upper Mississippi River Basin
Date
12/9/1996
Prepared By
USGS
Floodplain - Doc Type
Educational/Technical/Reference Information
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<br /> <br />42 <br /> <br />OVERVIEW OF RIVER-FLOODPLAIN ECOLOGY IN THE UPPER MISSISSIPPI RIVER BASIN <br /> <br />Van der Schalies' oversight of other late 1800's mussel <br />investigations and more recent mussel studies. <br />To evaluate temporal changes in the UMR mussel <br />fauna, Fuller (1980) compared the abundance of mussel <br />species in data collected by historical investigators with <br />data he collected in a 1977 survey. According to Fuller <br />(1980), four species have not been collected since about <br />1930 and a total of five since around 1900. Those five were <br />Tritigonia verrucosa, Potami/us capax. Venustaconcha <br />ellipsiformis, Alasmidonta marginata, and Simpsoniconcha <br />amhigua. even though S. amhigua has been collected more <br />recently at three UMR locations. <br />Although the actual number of mussel species has not <br />declined significantly since 1900, the abundance of certain <br />mussel fauna has changed drastically. The most docu- <br />mented case is that of the ebony shell (Fusconaia ehena), <br />which was once so abundant that it made up 80 percent of <br />the commercial shell industry (Coker, 1919). The ebony <br />shell depends upon the skipjack hening as the host fish for <br />part of its reproductive cycle. With the construction of the <br />hydroelectric dam at Keokuk, Iowa, in 1913, the skipjack <br />herring could no longer make spawning runs upriver and <br />serve as the host fish for ebony shell glochidia. The ebony <br />shell is still present but represented only by extremely old <br />individuals and thus is likely to disappear from the UMR. <br />The elephant ear (Elliptio crassidens) is in a similar <br />situation. <br />A cursory examination of the community composition <br />reveals that, historically, many species probably made up <br />only a small fraction of the original mussel assemblage. In <br />his examination of Ellis' (1931) survey, Fuller (1980) noted <br />that approximately two-fifths of the mussel species made up <br />less than I percent of the mussel population. The decline in <br />less common species was more evident in Fuller's 1977 sur- <br />vey (Fuller, 1978), which found that approximately one-half <br />of the species group mussel taxa made up less than I per- <br />cent of the fauna. Two species (Amhlema plicata and Trun- <br />cilia truncata) made up 48.88 percent of all the specimens <br />collected. Only 16 species showed some degree of stability <br />over the 50 years between Fuller's survey and that of Ellis <br />(1931). Lampsilis teres made up 13.8 percent of the popula- <br />tion in Ellis' survey but only 0.23 percent of Fuller's, <br />and Leptodea tragi/is similarly declined from 10.1 to <br />1.27 percent. Proptera alatus declined from 3.75 to 1.38 <br />percent. Fuller (1980) suggested that the decline of some <br />species (such as P. alatus) could reduce substrates (relict <br />shells) used by invertebrates (Le" aquatic insects) that serve <br />as food for other organisms. <br />Some species have increased in abundance but as a <br />result of negative changes caused by navigation improve- <br />ments. Truncilla donaciformis made up only 3.1 percent of <br />Ellis' collection but was the second most abundant in <br />Fuller's survey at 14.2 percent. Fuller theorized that <br />T. donaciformis populations were relatively low in the <br />1930's because the preferred habitat was found on dynamic <br /> <br />substrates that were eliminated as the riverbed meandered. <br />When more stable (less dynamic) backwaters were created <br />through navigation development, the species population <br />increased. <br />Comparison of the results of the Ellis survey with <br />those of Fuller's survey perfonned for the U.S. Anny Corps <br />of Engineers clearly shows that certain distinct alterations <br />impacted the mussel fauna during the intervening period of <br />about 50 years (Fuller, 1978). Although Potamilus capax <br />and Lampsilis higginsi have been listed as federally endan- <br />gered species. other species such as E/liptio crassidens are <br />equally as rare. Fuller (1980) described 50 UMR species on <br />the basis of their apparent health. Although admittedly sub- <br />jective, Fuller categorized 2 taxa as endangered, 21 jeopar- <br />dized, 12 troubled, and only 15 as healthy. Endangered <br />species were defined as taxa of a nationally protected spe- <br />cies group that are in danger of extinction throughout much <br />or all of their natural range. Jeopardized mussels face extir- <br />pation in the UMR for one or more reasons. including com- <br />mercial harvest, declining water quality, impoundment <br />(especially streambed change), and lack of suitable hosts. <br />Troubled species are those whose historical quantity and <br />(or) geographic range in the UMR have been reduced, but <br />each exhibits some evidence of reproduction. Fuller (1980) <br />attributed the decline of the mussel fauna to five factors: <br />waterway modification, streambed change, commercial har- <br />vest, declining water quality, and the Asiatic clam. <br />Several species that were marginally suited to the <br />UMR declined because they were unable to adapt to a mul- <br />titude of changes. Other species grew in abundance and (or) <br />dominance because of these changes. Overall, the number <br />of mussel species in the UMR assemblage has declined in <br />the last 50 years. <br />About the same time that Fuller was doing work on <br />UMR mussels, another survey of river union ids was being <br />perfonned by Perry (1979) for the Upper Mississippi River <br />Conservation Committee (UMRCC). Perry's survey was <br />more qualitative than those surveys perfonned by Grier and <br />Mueller (1922-1923), Van der Schalie and Van der Schalie <br />(1950), and Fuller (1980). Although Perry collected no har- <br />vest data, his findings of the species composition are similar <br />to Fuller's. Perry described 13 of the species collected as <br />common, compared with Fuller's description of only 15 <br />species as "healthy." Perry's description of factors contrib- <br />uting to the decline of mussel species agreed with that of <br />Fuller. <br />The previous discussion focused on changes to the spe- <br />cies composition of UMR mussel fauna. Little discussion <br />has been devoted to changes in the population related to <br />commercial harvest. Beginning about 1889, mussels were <br />harvested for their freshwater pearls and to make buttons for <br />the gannent industry. Like the gold rush, a frenzied search <br />began that resulted in an estimated $300,000 worth of pearls <br />being found by 1891 (O'Hara, 1980). Since freshwater <br />pearls are relatively rare, this search required the collection <br />
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