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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 />