PROTECTING WISCONSIN'S BIODIVERSITY

 
 
   
 
Community Name Global Rank State Rank Community Group

Wet-mesic Prairie

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Photo by Thomas Meyer

 

Counties with Mapped NHI Occurrences

This herbaceous grassland community is dominated by tall grasses, including big bluestem (Andropogon gerardii), Canada bluejoint grass (Calamagrostis canadensis), cordgrass (Spartina pectinata), and Canada wild-rye (Elymus canadensis). The forb component is diverse and includes azure aster (Symphyotrichum oolentangiense), eastern shooting-star (Primula meadia), saw-tooth sunflower (Helianthus grosseserratus), prairie blazing-star (Liatris pycnostachya), prairie phlox (Phlox pilosa), prairie coneflower (Ratibida pinnata), rosinweed and prairie-dock (Silphium integrifolium and S. terebinthinaceum), late and stiff goldenrods (Solidago gigantea and S. rigida), and Culver's-root (Veronicastrum virginicum). This community type was common historically but now is rare. Well over 99% of our tallgrass prairies - including wet-mesic prairies - have been destroyed.

Wet-mesic prairies sometimes occurred in large wetland complexes with wet prairies, southern sedge meadows, calcareous fens, and emergent marshes. They were most abundant on level or gently rolling glacial moraine or outwash landforms where there were few natural barriers to wildfire, and where the upland vegetation was composed mostly of fire-dependent communities such as mesic prairies and oak openings.

 
 
 

Wet-mesic prairies are characterized by their tall prairie grasses and forbs occurring on mineral soils in wetland complexes. Soils are usually loam, silt loam, or silty clay loam, which are sometimes overlain by a thin layer (<12 inches) of sandier soil. They can be distinguished from wet prairies by the greater prevalence of forbs associated with mesic and dry-mesic prairies such as yellow coneflower (Ratibida pinnata) and stiff goldenrod (Solidago rigida), and greater depth to water table. In contrast, wet prairies tend to have a higher water table and higher prevalence of wetland forbs such as Joe-Pye-weed (Eutrochium maculatum), boneset (Eupatorium perfoliatum), common water hemlock (Cicuta maculata), swamp milkweed (Asclepias incarnata), and water smartweed (Persicaria amphibia). Loamy soils set wet-mesic prairies apart from other similar wetland communities including calcareous fens and southern sedge meadows, both of which occur on organic soils (peat and/or marl). In addition, wet-mesic prairies are dominated by grasses in terms of biomass, where sedge meadows are dominated by sedges.

Wet-mesic prairies can be distinguished from mesic prairies because they are in wetland complexes, have heavier soils, and a higher prevalence of wetland plants, whereas mesic prairies tend to occur on well-drained soils (especially with loess) in level to rolling uplands and have a higher prevalence of upland forbs such as leadplant (Amorpha canescens), heath and smooth asters (Symphyotrichum ericoides, S. laeve), prairie coreopsis (Coreopsis palmata), prairie sunflower (Helianthus pauciflorus), rattlesnake-master (Eryngium yuccifolium), and spiderwort (Tradescantia ohioensis).

Species of Greatest Conservation Need (SGCN) are associated with habitats (or natural communities) and places on the landscape. Understanding relationships among SGCN, natural communities and ecological landscapes help us make decisions about issues affecting SGCN and their habitat and how to respond. Download the Wildlife Action Plan association score spreadsheet to explore rare species, natural communities and ecological landscape associations

Conservation actions respond to issues or threats, which adversely affect species of greatest conservation need (SGCN) or their habitats. Besides actions such as restoring wetlands or planting resilient tree species in northern communities, research, surveys and monitoring are also among conservation actions described in the Wisconsin Wildlife Action Plan because lack of information can threaten our ability to successfully preserve and care for natural resources.