PROTECTING WISCONSIN'S BIODIVERSITY

 
 
   
 
Community Name Global Rank State Rank Community Group

Southern Hardwood Swamp

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Photo by Ryan O'Connor

 

Counties with Mapped NHI Occurrences

Southern hardwood swamp is a forested wetland community type found in insular basins with seasonally high water tables. This type is best developed in glaciated southeastern Wisconsin but was not of large extent even prior to EuroAmerican settlement. Finley (1976) classified less than 1% of southeastern Wisconsin as lowland hardwood forest, and this figure includes bottomland forests along rivers as well as southern hardwood swamps in closed basins. Dominant tree species are silver maple (Acer saccharinum), red maple (Acer rubrum), hybrids of red and silver maples (e.g., Acer X freemanii), and green ash (Fraxinus pennsylvanica). Associate tree species may include swamp white oak (Quercus bicolor), bur oak (Q. macrocarpa) and their hybrids, basswood (Tilia americana), and American elm (Ulmus americana), all of which may be a significant part of the canopy or subcanopy in sites impacted by emerald ash borer. Black ash may be present in southern hardwood swamps but is usually not dominant across the site. The groundlayer is often dominated by species typical of floodplain forests 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). Southern hardwood swamps are also noted for a high component of lianas, including poison ivy (Toxicodendron radicans), Virginia creeper (Parthenocissus quinquefolia), and grapes (Vitis spp.). In the relatively undisturbed sites, there can be a rich spring flora. Microtopographic differences account for the existence of patches of spring ephemerals as well as many wetland species. The exotic reed canary grass (Phalaris arundinacea) has become dominant in the understory of many hardwood swamps.

This Natural Heritage Inventory community type partly includes the "southern wet-mesic forest" of the Curtis (1959) classification, although this Curtis type also includes the more common hardwood swamps usually maintained by groundwater seepage and dominated by black ash, red maple, American elm, and yellow birch. Curtis referred to this conglomerate type as "lacustrine forests" due to their frequent occurrence on lakeplains, both around the margins of larger existing lakes and on extinct glacial lakes, although southern hardwood swamps also occur in lower-lying portions of till plains that may not have held ponded water for any significant length of time during or after glaciation. Southern hardwood swamps are not restricted to southern Wisconsin, the name rather refers to their similarly to swamps more commonly found in the southern Midwest, especially those of the poorly drained till plains along the Ohio River valley.

 
 
 

Southern hardwood swamps are characterized by their seasonally high water tables that usually dry out by late summer, location in basins not associated with major rivers, and flora that is intermediate between floodplain forests and more northern hardwood swamps. They are distinguished from northern hardwood swamps by their vertically fluctuating water levels rather than a relatively stable supply of groundwater, thus lower proportion of peat (muck) soils due to soil drying out by mid-late summer allowing organic matter to decompose. They also tend to have a higher component of plant species that prefer these hydrologic conditions, such as those commonly found in floodplain forests (see description), whereas northern hardwood swamps have a higher prevalence of species preferring saturated soils such as marsh marigold (Caltha palustris), swamp raspberry (Rubus pubescens), orange jewelweed (Impatiens capensis), purple-stemmed aster (Symphyotrichum puniceum), lake sedge (Carex lacustris), blue-joint grass (Calamagrostis canadensis) as well as groundwater-loving species like bristle-stalked sedge (Carex leptalea), American golden saxifrage (Chrysosplenium americanum), and swamp saxifrage (Micranthes pensylvanica).

Southern hardwood swamps can be differentiated from floodplain forests by their occurrence in lakeplain basins or low-lying till plains rather than along major rivers (though they may occur near small streams), thus their water is supplied by rain and snowmelt rather than by overbank flooding. The lateral water movement in floodplain forests also leads to scouring, silt deposition and removal of organic detritus, processes that don't occur in southern hardwood swamps.

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.