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Whitford, Philip; Whitford, Kathryn (ed.) / Transactions of the Wisconsin Academy of Sciences, Arts and Letters
volume 74 (1986)

Keough, Janet R.
The Mink River- a freshwater estuary,   pp. 1-11 PDF (4.8 MB)

Page 10

10 Wisconsin Academy of Sciences, Arts and Letters [Vol. 74 
More protected communities, such as the wet meadow around the edge of the
wetland, are more species-rich. The wet meadow community develops on and
around Carex stricta hummocks; this topographic diversity, located higher
in the watershed, permits the establishment of more species. Keddy and Reznicek
(1985) suggested that the zonation of communities may be related to the position
of maximum and minimum high water. They suggest that certain communities—wet
meadow and shallow marsh—depend upon periodically exposed substrate
for seed establishment. This appears to be so in the Mink River system; only
those species that can survive by reproducing vegetatively persist in deep
water. Zizania aquatica requires mudflat conditions in spring to germinate.
Woody species on the shrub carr do not establish on hummocks, but in the
low spots on the wet meadow. They are repeatedly killed by high water. Regeneration
of such communities seems to be in phase with the cycle of low water conditions
in Lake Michigan. 
Little is known about the food web associated with Lake Michigan coastal
wetlands. Harris et a!. (1977) and Roznik (1978) have suggested that certain
birds may respond to the dynamic structure of these emergent plant communities
as water level changes from year to year. Furthermore, little is known about
how the chemical gradient along the river may influence the distribution
of aquatic plants or animals. Many intriguing questions can be raised concerning
long-term fluctuations in biomass production by the various plant communities,
as well as the fate of biomass and its contribution to the food web of the
river and bay. Much can be learned about the adaptations of organisms in
such a frequently disturbed coastal environment. Examples include the adaptations
to long-term waler level fluctuations by Carex stricta and Calamagrostis
canadensis, by species of Scirpus (S. americanum, S. acutus, and S. validus),
and by Zizania aquatica. While 
some coastal wetlands have been protected as natural reserves and are recognized
as including unusual species associations or unique habitats, many biological
and physical dynamics are still waiting to be explored. 
Forest Stearns is gratefully acknowledged for support and encouragement during
the entire course of this study, and, with Glenn Guntenspergen, offered many
helpful suggestions on the manuscript. Many thanks are due the faculty and
staff of the U.W. Center for Great Lakes Studies, whose equipment and expertise
made the field work possible. U.W.-Green Bay generously provided lodging
at Toft Point, under the administration of Keith White. Field assistance
was provided by many persons, the most persistent of whom included Joyce
Witebsky, Glenn Guntenspergen, and Steve Kroeger. Peter Salamun and Margaret
Summerfield helped with identification of submergent species. The study was
supported by a grant from the Wisconsin Coastal Management Program to Forest
Stearns and by the Raymond Hatcher Fund through the U.W.-Milwaukee Botany
Department. This is Contribution 289, U.W. Center for Great Lakes Studies.
Bosley, T. R. 1976. Green Bay's west shore coastal wetlands: a history of
change. M.S. Thesis. University of Wisconsin-Green Bay. 92 pp. 
Bosley, T. R. 1978. Loss of wetlands on the west shore of Green Bay. Trans.
Wis. Acad. Sci., Arts and Lett. 66:235-245. 
Brant, R. A. and C. E. Herdendorf. 1972. 
Delineation of Great Lakes estuaries. In Proc. 
15th Conf. Great Lakes Research., I. A. G. L. 
R., Ann Arbor, MI. pp. 710-7 18. 
Curtis, J. T. 1959. Vegetation of Wisconsin. University of Wisconsin Press,
Madison, WI. 657 pp. 
Dorr, J. A. Jr. and D. F. Eschman. 1977. Geology of Michigan. University
of Michigan Press, Ann Arbor. 475 pp. 
Fahselt, D. and M. A. Maun. 1980. A quan 

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