PROTECTING WISCONSIN'S BIODIVERSITY

 
 
   
 
Community Name Global Rank State Rank Community Group

Northern Hardwood Swamp

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Photo by Christina Isenring

 

Counties with Mapped NHI Occurrences

Northern hardwood swamps are deciduous forested wetlands that occur along lakes, streams, or in insular basins in poorly drained morainal landscapes. This community occurs across the state, but is most common in the northern ecological landscapes. The dominant tree species is black ash (Fraxinus nigra) but in some stands red maple (Acer rubrum), yellow birch (Betula alleghaniensis), and American elm (Ulmus americana) are also important. Some sites may also have a minor conifer component of northern white-cedar (Thuja occidentalis) or balsam fir (Abies balsamea). The tall shrub speckled alder (Alnus incana) may be locally common. The herbaceous flora is often diverse and may include many of the same species found in alder thickets. Typical species are marsh-marigold (Caltha palustris), swamp raspberry (Rubus pubescens), common skullcap (Scutellaria galericulata), orange jewelweed (Impatiens capensis), many sedges (Carex spp.), and groundwater-loving species like bristle-stalked sedge (Carex leptalea), American golden saxifrage (Chrysosplenium americanum), and swamp saxifrage (Micranthes pensylvanica). Soils may be mucks or mucky sands.

 
 
 

Northern hardwood swamps are characterized by relatively constant water levels, often with a groundwater component, and dominance by deciduous hardwood species, especially black ash. Relatively stable water levels lead to saturated soils that inhibit organic matter decomposition and the development of peat (muck) soils. They can be distinguished from southern hardwood swamps, which can also occur in northern Wisconsin, by their relatively stable water levels and higher prevalence of species that prefer saturated soils (see characteristic species above) while southern hardwood swamps are characterized by seasonally fluctuating water levels that usually drop by mid-later summer (similar to floodplains), higher proportion of mineral soils, and a higher prevalence of species that prefer these conditions such as Virginia wild-rye (Elymus virginicus), white grass (Leersia virginica), common wood-reed (Cinna arundinacea), wood nettle (Laportea canadensis), false nettle (Boehmeria cylindrica), and Ontario aster (Symphyotrichum ontarionis). Northern hardwood swamps can be differentiated from floodplain forests by their occurrence around lakes, basins in till plains, or headwater streams rather than along major rivers, and their prevalence of species that prefer saturated rather than seasonally inundated soils.

Northern hardwood swamps have many similarities with northern wet-mesic forests (cedar swamps), especially as both black ash and northern white-cedar can be canopy associates in both communities. In general, sites that are dominated by hardwoods are best typed as hardwood swamps, while areas dominated by conifers are best typed as northern wet-mesic forest, though both types may occur and intergrade across large wetland complexes.

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.