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UCREFRP
UCREFRP Catalog Number
8092
Author
U.S. Department of the Interior.
Title
Proceedings of the Symposium on Restoration Planning for the Rivers of the Mississippi River Ecosystem.
USFW Year
1993.
USFW - Doc Type
Washington, D.C.
Copyright Material
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<br />14 BIOLOGICAL REPoRT 19 <br /> <br />Table 4. Macroinvertebrate metricsa applied to <br />sampling stations in the Minnesota River basin. <br /> <br />Community metrics Taxonomic group metries <br /> <br />Richness Functional feeding group <br />ratio <br />Number and percent of <br />mayflies <br />Number and percent of <br />caddis flies <br />Number and percent of <br />dipterans <br />Ratio of mayflies, <br />stoneflies, caddis flies <br /> <br />Shannon-Weaver <br />Diversity Index <br />Equitability Index <br /> <br />Community Similarity <br />Index <br />Community Loss Index <br /> <br />Macroinvertebrate Biotic <br />Index <br /> <br />8Plafkin et aI. 1989. <br /> <br />river. The objective of this component of the project <br />was to assess the level of impairment among <br />macroinvertebrate communities throughout the <br />Minnesota River basin. <br />Benthic macroinvertebrates were collected at 9 <br />stations on the mainstem, 10 major tributaries, <br />and 22 minor watersheds. Benthic macroinverte- <br />brate sampling stations coincided with sampling <br />stations used for other project components. <br />Sampling gear consisted of hand picking, kick- <br />nets, and artificial substrate sampling (Hester and <br />Dendy 1962). Sampling was done in summer and <br />fall. Replicate samples were taken on some sites <br />on the mainstem and tributaries. <br />Eleven metrics are being used to assess the <br />health of the macroinvertebrate community at <br />each site (Plafkin et al; 1989). Six metries apply to <br />the whole community, and the other five apply to <br />specific taxonomic or functional groups (Table 4). <br />In addition to the biotic metrics, the habitat quality <br />of each site was quantified using a Qualitative <br />Habitat Evaluation Index (QHEI) developed by the <br />Ohio Environmental Protection Agency (1987). <br />In the 1989 sampling, chironomids dominated at <br />the most-downstream location (Henderson, rkm <br />108) and at the two most-upstream sites (Upper <br />Sioux, rkm 382; and Lac Qui Parle, rkm 454). At all <br />other mainstem stations, the communities were <br />dominated by caddis flies. The most common caddis <br />fly genus was Hydropsyche spp. Cheumatopsyche <br />spp. was collected in large numbers at Courtland <br />(rkm. 216), as was Cyrnellus spp. at Lac Qui Parle. <br />The most common chironomid genus on the main- <br />stem was Glyptotendipes, which was collected at all <br />stations. <br /> <br />Benthic community composition at tributary <br />sampling sites in 1989 varied more than at main- <br />stem sites. Caddis flies dominated at five sites, <br />chironomids at three, and mayflies at two. Other <br />major insect groups were generally found in higher <br />proporlions than on the mainstem. <br />In the 1990 survey, four mainstem sites were <br />dominated by caddis flies and midges, and one site <br />was dominated by mayflies. Chironomids again <br />dominated at Henderson, Upper Sioux, and Lac <br />Qui Parle. Glyptotendipes spp. was the most abun- <br />dant midge at five locations. <br />Community composition of benthos on the tribu- <br />taries was again more variable than on the main- <br />stem in the 1990 survey. Caddis flies were domi- <br />nant at five locations, mayflies at two, and midges <br />at three locations. <br />On the basis of richness, diversity, and macroin- <br />vertebrate biotic indices, the 19 stations on the <br />mainstem and tributaries were categorized in rela- <br />tion to the effects of pollution. All stations sampled <br />in 1989 and 1990 were affected by pollution, as <br />determined by the three metries listed above (Table <br />5). Henderson, Upper Sioux, and Lac Qui Parle <br />were the mainstem stations most affected, while <br />the Chippewa River was the most affected tribu- <br />tary. <br />Comparison of benthic diversity indices with <br />QHEI indicates a relation between the two in the <br />tributaries. As QHEI increased, diversity increased <br />in 1989 and 1990. There was no such relationship <br />observed in the mainstem sites. Perhaps the main- <br />stem sites are more affected by variables other than <br />habitat, with respect to macroinvertebrates. <br /> <br />Fish Physiology <br /> <br />Organic pollutants have the ability to induce <br />liver mixed-function oxidase activities in fish <br />(Brown 1976; Melancon et al. 1987). Polychlori- <br />nated biphenyls have been found in fish from the <br />Minnesota River by the Minnesota Department of <br />Health. Levels of PCB's were high enough to issue <br />consumption advisories for sport-caught fish. <br />From Granite Falls to the mouth of the river, the <br />advisory for most fish is one meal per month. <br />The objective of this component of the study was <br />to determine if PCB's alone or in combination with <br />other organic pollutants in the Minnesota River <br />were sufficient to have a significant effect on fish <br />liver activities. An additional objective was to com- <br />pare PCB levels found through arochlor analysis <br />versUS congener analysis. <br />
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