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Habitat Description
Habitat Crosswalk
Cowardin: Palustrine; emergent wetland, persistent (Cowardin et al. 1979).
Shaw and Fredine: Type 2: Inland fresh meadow (Shaw and Fredine 1971).
Vegetation of Wisconsin: Northern and southern sedge meadow (Curtis 1971).
Wisconsin Department of Natural Resources Natural Communities: Northern Sedge Meadow, Shore Fen, Central Poor Fen, Poor Fen (WDNR 2005).
Wisconsin Wetland Inventory: Emergent/wet meadow, narrow-leaved persistent (WDNR 1992).
Introduction
Northern Sedge Marsh is a wetland community co-dominated by sedges, spike-rushes, bluejoint grass, and emergent vegetation with at least 20% open water. Northern Sedge Meadow is an open wetland community dominated by sedges and grasses with woody cover <5% (Sample and Mossman 1997). Northern sedge meadows vary widely in plant composition across their range and are categorized in two distinct subtypes: tussock meadow densely vegetated with tussock sedge and broad-leaved sedges such as common lake sedge, beaked sedge,and common yellow lake sedgeand wire-grass sedge meadow sparsely vegetated with bluejoint grass and thin wire-grass sedges such as few-seeded sedgeand narrow-leaved woolly sedge (Mossman and Sample 1990). Forb species common to both subtypes include arrow-leaved tear-thumb, purple-stem aster, common flat-topped goldenrod, and rough bedstraw (Curtis 1971, Mossman and Sample 1990). Species that characterize northern but not southern sedge meadows include fringed brome, bulblet water-hemlock, rattlesnake grass, northern blue flag, northern bugleweed, and meadow willow. Northern sedge meadows also feature higher densities of bulrushes such as black bulrush (Curtis 1971) and occasionally support a sphagnum moss groundcover similar to but less continuously distributed than in open bogs (WDNR 2005).
Historical and Present-day Context and Distribution
Sedge meadows historically covered approximately 459,000 hectares in Wisconsin. Today, approximately 12,000 hectares (3%) remain in moderate to high quality condition. Although many of the remaining meadows are highly fragmented, some large tracts such as Crex Meadows State Wildlife Area persist along and north of the tension zone (Mossman and Sample 1990). Northern sedge meadows occur in extinct glacial lake beds, depressions in glacial moraines or pitted outwash, and around lake and stream shorelines (Curtis 1971).
Natural Disturbances and Threats
Sedge meadows and marshes frequently exist in a state of transition and thus are highly sensitive to hydrologic disruption. Natural succession to an herb-dominated or shrub-dominated wetland community can occur with either prolonged drought or flooding. Emergent marsh may replace sedge meadow at sites experiencing extended periods of soil saturation, such as cranberry farms or other publicly-owned water impoundments. Sites with drier conditions may support higher shrub densities and succeed to an alder thicket or shrub-carr community. Wildfire may have limited this woody encroachment and maintained historic northern sedge meadow habitats in Wisconsin, particularly within the fire-prone landscapes of Northwest Sands and Central Sand Plains. Widespread fire suppression policies enacted in the first half of the twentieth century, especially when they coincided with wetland drainage schemes, likely expedited the conversion of sedge meadow to shrub swamp or lowland forest (E. Epstein, pers. comm.).
Differences in substrate also may contribute to differences in the plant composition and successional sequence of sedge meadows and marshes. Some northern sedge meadows may eventually succeed to conifer swamp or other peatland communities, depending upon the nature and depth of the peat (Mossman and Sample 1990). Sedimentation caused by urban development, agriculture, and grazing may reduce the microtopography required by native sedge meadow species and facilitate invasive species establishment. Reed canary grass and cat-tail in particular can form monospecific colonies that simplify the plant composition of northern sedge meadow and marsh communities (Werner and Zedler 2002).
Related WBCI Habitats: Southern Sedge Meadow and Marsh, Open Bog-Muskeg, Shrub-carr, Alder Thicket, Emergent Marsh.
Overall Importance of Habitat for Birds
Despite their structural simplicity, sedge meadows and marshes are very important to Wisconsin’s avifauna as they contain several habitat specialists and species of high conservation priority. Nelson’s Sharp-tailed Sparrow, Le Conte’s Sparrow, and Yellow Rail are considered specialists of this habitat type and American Bittern and Sedge Wren are more abundant in sedge meadows than any other habitat type in Wisconsin. The American Bittern increases in sedge meadows with wetter conditions (Mossman and Sample 1990, Robbins 1991, Dechant et al. 2003a) while Sedge Wren presence is positively correlated with maximum height of vegetation, herbaceous cover, and “standing residual cover” (Sample 1989).
Other species have less specific requirements and may occur in a variety of wet grassland habitats. However, as the quality and extent of these other habitats continues to decline, sedge meadow complexes become increasingly important in providing stable habitat for these species. The grassland-associated Bobolink has been significantly impacted by the loss of its preferred habitats and may become more reliant on the remaining sedge meadows in the state. Area-sensitive grassland species such as Northern Harrier, Sharp-tailed Grouse, Yellow Rail, Short-eared Owl, and possibly Nelson’s Sharp-tailed Sparrow and Wilson’s Phalarope, also take refuge in northern sedge meadow habitats as the surrounding landscape becomes progressively more fragmented (Mossman and Sample 1990).
Northern sedge marshes (as distinct from meadows) are characterized by a mixture of meadow and marsh conditions and support a few species that require open water. Red-necked Grebe, Trumpeter Swan, Black Tern, and Blue-winged Teal are all characteristic nesting species of most sedge marshes in northern and central Wisconsin. Sedge marshes also provide habitat for migratory waterbirds, waterfowl, and shorebirds. In particular, shorebirds use the shallow mudflats exposed after managed drawdowns or natural water level fluctuations (Mossman and Sample 1990).
Priority Birds
Species Status Habitat and/or Special Habitat Features Canada Goose
(Mississippi Valley Population)M Trumpeter Swan B Breeds in sedge marshes with abundant submerged aquatic plants. American Black Duck b, m Nests in areas interspersed with emergent vegetation and open water. Mallard B, M Requires adjacent upland habitat for nesting. Northern Pintail b, m Prefers areas interspersed with emergent vegetation and open water. Blue-winged Teal B, M Requires adjacent upland habitat for nesting. Lesser Scaup m Hooded Merganser b, m If nest cavities available nearby. American Bittern B Found in sedge meadows and marshes >20 ha. Great Egret f, m Forages during post-breeding movements in sedge marshes. Snowy Egret m Rare migrant in sedge marshes. Osprey f Forages in sedge marshes with fish populations. Bald Eagle F Forages in sedge marshes with fish populations. Northern Harrier B, M Found on larger sedge meadow/marsh sites. Sharp-tailed Grouse b, m, w Large sedge meadow complexes. Greater Prairie-Chicken b, m, w Yellow Rail b, m Specialist; prefers larger wiregrass sedge meadows and marshes. Whooping Crane b, f Assumed that this species will one day breed and forage in this type. American Golden-Plover m Found in sedge marshes with exposed mudflats. Greater Yellowlegs M Found in sedge marshes with exposed mudflats. Solitary Sandpiper M Found in sedge marshes with exposed mudflats. Whimbrel m Found in sedge marshes with exposed mudflats. Hudsonian Godwit m Found in sedge marshes with exposed mudflats. Marbled Godwit m Found in sedge marshes with exposed mudflats. Buff-breasted Sandpiper m Found in sedge marshes with exposed mudflats. Short-billed Dowitcher m Found in sedge marshes with exposed mudflats. Wilson’s Phalarope b, m Requires some standing water and large tracts. Black Tern b Needs larger sedge marshes with floating nesting substrate. Short-eared Owl b, m, w Very rare nester; forages in large sedge meadows during migration and winter. Sedge Wren B Prefers stands of tall, dense vegetation with a dense litter layer. Common Yellowthroat B Prefers tall, rank herbaceous cover. Le Conte’s Sparrow B Specialist; prefers wiregrass sedge meadows and marshes Nelson’s Sharp-tailed Sparrow b Specialist; prefers wiregrass sedge meadows in northwest Wisconsin. Swamp Sparrow B Prefers tall, rank herbaceous cover. Bobolink B Common breeder in larger sedge meadow areas.
Objectives
Stay tuned……. will incorporate habitat acreage objectives from Upper Mississippi River and Great Lakes Region Joint Venture Implementation Plan.
Management Recommendations
Landscape-level Recommendations
- Maintain and protect sedge meadow complexes >40 ha to provide habitat for area-sensitive species like Northern Harrier, Yellow Rail, Short-eared Owl, and American Bittern (Mossman and Sample 1990, Sample and Mossman 1997, Dechant et al. 2003a, Dechant et al. 2003b, WDNR 2005).
- Where applicable, maintain sedge meadows in conjunction with open bogs, muskegs, poor fens, and other open habitats to protect hydrological function and provide for a diverse suite of species (WDNR 2005).
- Maintain wetland function and biodiversity by minimizing impervious surfaces, limiting development, and reducing soil loss and nutrient delivery within watersheds.
- Encourage wetland management, protection, and restoration efforts on private lands through existing federal and state programs and by educating private landowners on wetland stewardship.
Site-level Recommendations
- Avoid soil disturbance (e.g., pothole creation, heavy grazing, or construction of level ditches) within this type to prevent the establishment of invasive plant species (WDNR 2005).
- Avoid habitat conversion by properly managing water levels within sedge meadows (i.e., avoid permanent flooding or drainage; Mossman and Sample 1990, WDNR 2005).
- Use prescribed fire or mechanical treatments on a periodic basis to prevent woody invasion in sedge meadow habitats (WDNR 2005).
- Because site conditions vary, develop property-specific plans to control invasive species such as reed canary grass and cat-tail (see http://www.dnr.wi.gov/org/water/fhp/wetlands/resman.shtml).
Ecological Opportunities
Ecological Landscape Opportunity Management Recommendations Central Sand Plains Major All North Central Forest Major All Northern Highland Major All Northern Lake Michigan Coastal Major All Northwest Lowlands Major All Northwest Sands Major All Central Lake Michigan Coastal Important All Central Sand Hills Important All Forest Transition Important All Northeast Sands Important All Southeast Glacial Plains Important All Superior Coastal Plain Important All Western Coulee and Ridges Important All Western Prairie Present All
Research Needs
- Implement a marshbird monitoring program to adequately measure abundance, distribution, population status, and habitat use of key species within northern sedge meadows and marshes.
- Identify sedge meadows and marshes in need of protection, restoration, and/or management within all ecological landscapes.
- Investigate the effects of different management regimes such as fire, mowing, or passive management on nesting sedge meadow birds in Wisconsin.
- Determine appropriate water level management, including timing of high and low water, to maintain this natural community.
- Monitor sedge meadow and marsh restoration and enhancement activities to assess their wildlife value and adaptively refine management activities.
- Study the role of beaver in maintaining (or inundating) sedge meadows.
Implementation
Key Sites
- Bear Bluff Peatlands (Jackson, Wood, Juneau Cos.)
- Bear Lake Sedge Meadow (Barron Co.)
- Bibon Swamp (Bayfield Co.)
- Central Northern Highlands (Vilas, Oneida Co.)
- Crex Meadows State Wildlife Area (Burnett Co.)
- Fish Lake Wetlands and Barrens (Burnett Co.)
- George W. Mead State Wildlife Area (Marathon, Portage, Wood Cos.)
- Green Bay West Shore Wetlands (Brown, Oconto, Marinette Cos.)
- Kakagon-Bad River Wetlands and Forest Corridor (Ashland Co.)
- Lower Peshtigo River (Marinette Co.)
- Manitowish Peatlands (Iron, Vilas Cos.)
- Mink River Estuary-Newport State Park (Door Co.)
- Moose Junction Peatlands (Douglas Co.)
- Owen-Teal Forest (Bayfield, Sawyer Cos.)
- Rainbow Flowage and Peatlands (Oneida Co.)
- South Shore Wetlands (Bayfield Co.)
- Toft Point-Ridges Sanctuary-Mud Lake (Door Co.)
Key Partners
- Ducks Unlimited: http://www.ducks.org/
- Natural Resources Conservation Service (NRCS): http://www.nrcs.usda.gov/
- The Nature Conservancy: http://www.nature.org/
- U.S. Fish and Wildlife Service: http://www.fws.gov/
- Wisconsin Department of Natural Resources: http://www.dnr.state.wi.us/
- Wisconsin Wetlands Association: http://www.wisconsinwetlands.org/
Funding Sources
- Federal Duck Stamp Program: http://www.fws.gov/duckstamps/
- Knowles-Nelson Stewardship Program: http://dnr.wi.gov/stewardship/
- North American Wetlands Conservation Act (NAWCA): http://www.fws.gov/birdhabitat/NAWCA/grants.htm
- Partners for Wildlife program (PFW): http://www.fws.gov/midwest/WisconsinPartners/index.htm
- Wetland Reserve Program (WRP): http://www.nrcs.usda.gov/programs/wrp/
- Wisconsin Waterfowl Stamp Program: http://www.dnr.state.wi.us/org/land/wildlife/regs/index.htm
Information Sources
- Chadde, S.W. 1998. A Great Lakes wetland flora: a complete, illustrated guide to the aquatic and wetland plants of the Upper Midwest. Pocketflora Press, Calumet, MI. 569 pp.
- Czarpata, E.J. 2005. Invasive plants of the Upper Midwest. University of Wisconsin Press, Madison, WI. 215 pp.
- Effects of management practices on grassland birds: http://www.npwrc.usgs.gov/resource/literatr/grasbird/index.htm
- Effects of management practices on wetland birds: http://www.npwrc.usgs.gov/resource/literatr/wetbird/index.htm
- Eggers, S.D. and D.M. Reed. 1987. Wetland plants and plant communities of Minnesota and Wisconsin. U.S. Army Corps of Engineers, St. Paul District, St. Paul, MN. 201 pp.
- Linde, A.F. 1969. Techniques for wetland management. Wisconsin Department of Natural Resources Research Report No. 45. Madison, WI. 156 pp.
- Managing Habitat for Grassland Birds: A Guide for Wisconsin: http://www.npwrc.usgs.gov/resource/birds/wiscbird/
- Northern Prairie Wildlife Research Center wetland habitat crosswalk: http://www.npwrc.usgs.gov/resource/plants/mnplant/tab1.htm
- Reversing the Loss: a strategy for protecting and restoring wetlands in Wisconsin: http://dnr.wi.gov/org/water/fhp/wetlands/documents/reversing.pdf
- Wetland Restoration Handbook for Wisconsin Landowners (2nd edition): http://www.dnr.wi.gov/org/water/fhp/wetlands/resman.shtml
- Wetter, W.A., T.S. Cochrane, M.R. Black, H.H. Iltis, and P.A. Berry. 2001. Checklist of the vascular plants of Wisconsin. Technical Bulletin 192.
- Wisconsin Department of Natural Resources Best Management Practices: http://dnr.wi.gov/org/land/forestry/Usesof/bmp/
- Wisconsin State Herbarium: http://www.botany.wisc.edu/herbarium/
- Wisconsin Wetlands Association wetland habitat crosswalk: http://www.wisconsinwetlands.org/CommunityCrosswalk.pdf
References
- Cowardin, L. M., V. Carter, F. C. Golet, E. T. LaRoe. 1979. Classification of wetlands and deepwater habitats of the United States. U. S. Department of the Interior, Fish and Wildlife Service, Washington, D.C. Jamestown, ND: Northern Prairie Wildlife Research Center Home Page http://www.npwrc.usgs.gov/resource/1998/classwet/classwet.htm (Version 04DEC98).
- Curtis, J.T. 1971. The vegetation of Wisconsin: an ordination of plant communities. Univ. of Wisconsin Press, Madison, WI.
- Dechant, J.A., M.L. Sondreal, D.H. Johnson, L.D. Igl, C.M. Goldade, A.L. Zimmerman, and B.R. Euliss. 2003a. Effects of management practices on grassland birds: American Bittern. Northern Prairie Wildlife Research Center, Jamestown, ND. Northern Prairie Wildlife Research Center http://www.npwrc.usgs.gov/resource/literatr/grasbird/ambi/ambi.htm.
- Dechant, J.A., M.L. Sondreal, D.H. Johnson, L.D. Igl, C.M. Goldade, M.P. Nenneman, and B.R. Euliss. 2003b. Effects of management practices on grassland birds: Short-eared Owl. Northern Prairie Wildlife Research Center, Jamestown, ND. Northern Prairie Wildlife Research Center Online. http://www.npwrc.usgs.gov/resource/literatr/grasbird/seow/seow.htm (Version 12DEC2003).
- Mossman, M.J. and D.W. Sample. 1990. Birds of Wisconsin sedge meadows. Passenger Pigeon 52(1): 39-55.
- Robbins, S.D., Jr. 1991. Wisconsin birdlife: Population and distribution past and present. Madison, WI: Univ. Wisconsin Press.
- Sample, D.W. 1989. Grassland birds in southern Wisconsin: habitat preference, population trends, and response to land use changes. Unpublished M.S. thesis. University of Wisconsin, Madison, Wisconsin.
- Sample, D.W. and M.J. Mossman. 1997. Managing habitat for grassland birds: a guide for Wisconsin. Bureau of Integrated Science Services, Department of Natural Resources, Madison, WI.
- Shaw, Samuel and C. Gordon Fredine. 1971. Wetlands of the United States. Circular 39. U.S. Department of the Interior, U.S. Fish and Wildlife Service, Washington, D.C. 67 pp.
- Werner, K.J. and J.B. Zedler. 2002. How sedge meadow soils, microtopography, and vegetation respond to sedimentation. Wetlands 22(3): 451-466.
- Wisconsin Department of Natural Resources (WDNR). 1992. Wisconsin wetland inventory classification guide. Wisconsin Department of Natural Resources Publ-WZ-WZ023.
- Wisconsin Department of Natural Resources (WDNR). 2005. Wisconsin’s Strategy for Wildlife Species of Greatest Conservation Need. Madison, WI.
Contact Information
- Compiler: William P. Mueller, iltlawas@earthlink.net
- Editor: Kim Kreitinger, K.Kreitinger@gmail.com