PROTECTING WISCONSIN'S BIODIVERSITY

 
 
   
 
Community Name Global Rank State Rank Community Group

Northern Wet-mesic Forest

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Photo by Andy Clark

 

Counties with Mapped NHI Occurrences

This forested minerotrophic wetland is dominated by northern white-cedar (Thuja occidentalis) and occurs on rich, neutral to alkaline peats and mucks throughout much of northern Wisconsin. Balsam fir (Abies balsamea), black ash (Fraxinus nigra), and spruces (Picea glauca and P. mariana) are among the many potential canopy associates. The understory is rich in mosses, lichens, liverworts, ferns, sedges (such as Carex disperma and C. trisperma), orchids (e.g., Platanthera obtusata and Listera cordata), and wildflowers such as goldthread (Coptis trifolia), fringed polygala (Polygala pauciflora), and naked miterwort (Mitella nuda), and trailing sub-shrubs such as twinflower (Linnaea borealis) and creeping snowberry (Gaultheria hispidula). A number of rare plants occur more frequently in the cedar swamps than in any other habitat. Older cedar swamps are often structurally complex, as the easily wind-thrown cedars are able to continue growing with now-vertical branches growing into new trees and developing new root systems where the trunk is buried in the soil. Some of the canopy associates (especially white spruce as well as the occasional white pine) have the potential to reach heights considerably beyond those usually attained by cedar, producing a multi-layered canopy. The tall shrub layer is often well-developed and may include speckled alder (Alnus incana), alder-leaved buckthorn (Rhamnus alnifolia), wild currants (Ribes spp.), and mountain maple (Acer spicatum). Canada yew (Taxus canadensis) was formerly an important tall shrub in cedar swamps but is now rare or local due to deer browsing.

Seepages, springs, and spring runs contribute to stand complexity and provide critical habitat for additional plants and animals. Cedar swamps are relatively common in depressions that receive mineral-enriched groundwater, and can be associated with both ground moraine and outwash landforms.

 
 
 

Northern wet-mesic forests are characterized by calcium-rich neutral to alkaline peat or muck soils, usually with a strong groundwater component and a canopy dominated by northern white-cedar. They are most similar to northern hardwood 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 sites dominated by conifers are best typed as northern wet-mesic forest, though both types may occur and intergrade across large wetland complexes. Northern wet-mesic forests also have some similarities with northern tamarack swamps but are more minerotrophic and dominated by northern white-cedar rather than tamarack, though tamarack may be a minor component of some cedar swamps. Northern wet-mesic forests often occur in forested swales associated with Great Lakes ridge and swale community complexes. In these cases, they would be classified a component of the larger ridge and swale community.

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.