* limited to sites with higher soil calcium
Vascular plant nomenclature follows Rhoads and Block (2007). Bryophyte nomenclature follows Crum and Anderson (1981).

International Vegetation Classification Associations:

USNVC Crosswalk:

None

Representative Community Types:

Northern Peatland Shrub Swamp (CEGL006158)

NatureServe Ecological Systems:

Boreal-Laurentian Bog (CES103.581)

NatureServe Group Level:

None

Origin of Concept

Zimmerman, E., and G. Podniesinski. 2008. Classification, Assessment and Protection of Floodplain Wetlands of the Ohio Drainage. Pennsylvania Natural Heritage Program, Western Pennsylvania Conservancy, Pittsburgh, PA. Report to: The United States Environmental Protection Agency and the Pennsylvania Department of Conservation and Natural Resources, Office of Conservation Science. US EPA Wetlands Protection State Development Grant no. CD-973081-01-0.

Pennsylvania Community Code*

SS : Alder – Sphagnum Wetland

*(DCNR 1999, Stone 2006)

Similar Ecological Communities

Acidic Mixed Shrub – Sphagnum Wetland differs from Circumneutral Mixed Shrub Wetland in that the Acidic Mixed Shrub – Sphagnum Wetland occupies the lower end of the pH spectrum while the latter is circumneutral to somewhat calcareous. The associate species reflect this shift, with acidophiles such as highbush blueberry (Vaccinium corymbosum) and maleberry (Lyonia ligustrina) occurring as associate species in the Acidic Mixed Shrub – Sphagnum Wetland, while shrubs like dogwoods (Cornus spp.) and viburnums (Viburnum spp.) occur in a more circumneutral setting. The presence of a substantial sphagnum layer within the Acidic Mixed Shrub – Sphagnum Wetland generally distinguishes the two community types.

Fike Crosswalk

Alder - sphagnum wetland

Conservation Value

This community may serve as important habitat for breeding birds, including woodcocks (Scolopax minor) and yellow-bellied flycatchers. Plant species of conservation concern may include screwstem (Bartonia paniculata) and Mountain Alder (Alnus viridis).

Threats

Acidic Mixed Shrub – Sphagnum Wetlands are threatened by habitat alteration (e.g., conversion to agricultural land, logging in adjacent uplands), deposition (e.g., sedimentation, nutrient loading), and alterations to the hydrological regime (e.g., removal of beaver dams or other impoundments, lowering of the water table). Invasive species such as reed canary-grass (Phalaris arundinacea) may alter the species composition of this community type.

Management

A natural buffer around the wetland should be maintained in order to minimize nutrient runoff, pollution, and sedimentation. Soil erodibility in terms of the soil texture, condition of the adjacent vegetation (mature forests vs. clearcuts) and the topography of the surrounding area (i.e. degree of slope) should be considered when establishing buffers. Impervious surfaces surrounding the wetland should be minimized to prevent thermal pollution. Direct impacts and habitat alteration should be avoided (e.g., roads, trails, filling of wetland) and low impact alternatives (e.g., elevated footpaths, boardwalks, bridges) should be utilized in situations where accessing the wetland can not be avoided. Care should also be taken to control and prevent the spread of invasive species within the wetland. Alterations to groundwater sources should be minimized.

Acidic Mixed Shrub – Sphagnum Wetland is one example of declining shrubland habitat found in Pennsylvania. Shrubland habitats are early successional plant communities, often formed by disturbance event(s), which represent a short-lived transitional stage between more stable community types. Repeated disturbance events over time (either natural or anthropogenic) are needed to reset the community back to its earlier successional state. In the absence of disturbance, shrubland habitats may only remain a component of the landscape for 15-20 years before reverting to young forests. Shrublands provide habitat for many early successional-dependent species such as birds. Management activities such as removal of tree species, assisted disturbance, and invasive species control may be needed to maintain this community type.

Range Map

Pennsylvania Range

This community is found in the entire state except within the Coastal Plains.

Global Distribution

Pennsylvania, New York, New Hampshire, Vermont, Maine, and possibly Massachusetts and extends into eastern Canada.

Fike, J. 1999. Terrestrial and palustrine plant communities of Pennsylvania. Pennsylvania Natural Diversity Inventory. Harrisburg, PA 79 pp.

NatureServe 2010. NatureServe Explorer: An online encyclopedia of life Version 7.1. NatureServe, Arlington, VA. Available http://www.natureserv.org/explorer (accessed: 23 November 2011).

Pennsylvania Department of Conservation and Natural Resources (DCNR). 1999. Inventory Manual of Procedure. For the Fourth State Forest Management Plan. Pennsylvania Bureau of Forestry, Division of Forest Advisory Service.  Harrisburg, PA. 51 ppg.

Stone, B., D. Gustafson, and B. Jones. 2006 (revised). Manual of Procedure for State Game Land Cover Typing.  Commonwealth of Pennsylvania Game Commission, Bureau of Wildlife Habitat Management, Forest Inventory and Analysis Section, Forestry Division.  Harrisburg, PA. 79 ppg.