Print Report
G804 Dasiphora fruticosa - Carex lasiocarpa Eastern Boreal Alkaline Fen Group
Type Concept Sentence: These fens, distributed across eastern boreal regions of North America, develop in open basins where lateral groundwater flow through circumneutral to calcareous parent materials creates moderately to strongly alkaline conditions.
Common (Translated Scientific) Name: Shrubby-cinquefoil - Woolly-fruit Sedge Eastern Boreal Alkaline Fen Group
Colloquial Name: Eastern North American Boreal Alkaline Fen
Hierarchy Level: Group
Type Concept: [The concept for this group is under review with Canadian ecologists; the current concept overlaps with ~Eastern North American Subboreal Alkaline Fen Group (G185)$$.] These fens, distributed across eastern boreal regions of North America, develop in open basins where lateral groundwater flow through circumneutral to calcareous parent materials creates moderately to strongly alkaline conditions. They are found on level to gently sloping surfaces, or in closed wet depressions (sometimes as floating mats), and along wetland margins and lakeshores and rivershores. The shore fens are occasionally flooded, and so are included here because flooding tends to create moderately alkaline conditions. The vegetation may be graminoid-dominated, shrub-dominated, or a patchwork of the two, with broad-leaved non-ericaceous shrubs typically dominant. There is a discontinuous to absent layer of Sphagnum peatmoss (<80% cover), with brown mosses (Calliergon, Campylium, Drepanocladus, Tomentypnum) present to dominant. Broad-leaved non-ericaceous shrubs (Alnus incana, Betula glandulosa, Betula pumila, Dasiphora fruticosa ssp. floribunda, Myrica gale, Salix spp.) exceed cover of ericaceous shrubs, although some shore fens may be dominated by Chamaedaphne calyculata. Thin-leaved graminoids include Carex interior, Carex lasiocarpa, Carex limosa, Carex livida, Eriophorum viridicarinatum, Muhlenbergia glomerata, and Trichophorum alpinum. In the tree layer, Picea mariana is rare to absent and Larix laricina is variable. Minerotrophic Sphagnum dominates the substrate among medium fens, but brown mosses become increasingly common under richer conditions. Campylium stellatum is an indicator brown moss bryophyte.
Diagnostic Characteristics: This type contains a moss peat layer with depths exceeding 40 cm. Dwarf-shrubs and thin-leaved graminoids are >25%, and trees <25%. There is a discontinuous to absent layer of Sphagnum peatmoss (<80% cover), with brown mosses (Calliergon, Campylium, Drepanocladus, Tomentypnum) present to dominant. Broad-leaved non-ericaceous shrubs (Alnus incana, Betula glandulosa, Betula pumila, Dasiphora fruticosa ssp. floribunda, Myrica gale, Salix spp.) exceed cover of ericaceous shrubs, although some shore fens may be dominated by Chamaedaphne calyculata. Thin-leaved graminoids include Carex interior, Carex lasiocarpa, Carex limosa, Carex livida, Eriophorum viridicarinatum, Muhlenbergia glomerata, and Trichophorum alpinum, and together these graminoids exceed the cover of acidic peatland graminoids indicators (Carex magellanica ssp. irrigua, Carex oligosperma, Eriophorum vaginatum, Eriophorum virginicum, Scheuchzeria palustris). In the tree layer, Picea mariana is rare to absent and Larix laricina is variable.
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: The concept for this group is under review with Canadian ecologists; the current concept overlaps with ~Eastern North American Subboreal Alkaline Fen Group (G185)$$. This type contains a moss peat layer with depths exceeding 40 cm. Dwarf-shrubs and thin-leaved graminoids are >25%, and trees <10%. There is a discontinuous to absent layer of Sphagnum peatmoss (<80% cover), with brown mosses (Calliergon, Campylium, Drepanocladus, Tomentypnum) present to dominant. Broad-leaved non-ericaceous (Alnus incana, Betula glandulosa, Betula pumila, Dasiphora fruticosa ssp. floribunda, Myrica gale, Salix spp.) exceed cover of ericaceous shrubs, although some shore fens may be dominated by Chamaedaphne calyculata. Thin-leaved graminoids include Carex interior, Carex lasiocarpa, Carex limosa, Carex livida, Eriophorum viridicarinatum, Muhlenbergia glomerata, and Trichophorum alpinum, and together these graminoids exceed the cover of acidic peatland graminoid indicators (Carex magellanica ssp. irrigua, Carex oligosperma, Eriophorum vaginatum, Eriophorum virginicum, Scheuchzeria palustris). In the tree layer, Picea mariana is rare to absent and Larix laricina is variable.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: This group contains a moss peat layer with depths exceeding 40 cm. Dwarf-shrubs and thin-leaved graminoids are >25%, and trees <25%. There is a discontinuous to absent layer of Sphagnum peatmoss (<80% cover), with brown mosses present to dominant. Ericaceous dwarf-shrubs are typically minor, with broad-leaved shrubs dominant. Broad-leaved non-ericaceous shrubs exceed cover of ericaceous shrubs (>50%), although some shore fens may be more ericaceous-dominated. Thin-leaved graminoids are common. The tree layer is rare to absent (though some treed fens may fall within this group).
The landscape morphology of alkaline peatlands is often very striking. A variety of approaches has been taken to describe these forms: in Maine, see Davis and Anderson (2001); in Canada, see National Wetlands Working Group (1988); and in Minnesota, see Glaser (1992a). In Canada, bog and fen peatlands each have their own set of forms. In Minnesota, Glaser treats bogs and fens together as part of larger patterned peatland complexes (mire complexes). Particularly distinctive are the ribbed bogs or fens in which a pattern of narrow (2- to 3-m wide), low (<1 m deep) ridges are oriented at right angles to the direction of the drainage (National Wetlands Working Group 1988). Wet pools or depressions occur between the ridges. These patterned peatlands may include string bog, Atlantic ribbed fen, or northern ribbed fen (National Wetlands Working Group 1988). They develop almost entirely north of 46°N latitude in east-central Canada and the adjacent U.S. They are minerotrophic peatlands in which the vegetation has developed into a pattern of strings (raised, usually linear features) and flarks (wet depressions separating the strings). The substrate chemistry is entirely acidic in some peatlands; in others, where bedrock or other substrate influence creates circumneutral to calcareous conditions, peatland chemistry may be entirely calcareous or vary from acidic to calcareous within the same peatland. In acidic portions, typical bog heaths predominate mixed with sedges. Dasiphora fruticosa ssp. floribunda is diagnostic of circumneutral to calcareous conditions. These peatlands usually develop in open basins and flat plains, and the patterned portion may occupy only a fraction of the entire peatland. The edge of the basin may be shallow to deep peat over a sloping substrate, where seepage waters provide nutrients.
The landscape morphology of alkaline peatlands is often very striking. A variety of approaches has been taken to describe these forms: in Maine, see Davis and Anderson (2001); in Canada, see National Wetlands Working Group (1988); and in Minnesota, see Glaser (1992a). In Canada, bog and fen peatlands each have their own set of forms. In Minnesota, Glaser treats bogs and fens together as part of larger patterned peatland complexes (mire complexes). Particularly distinctive are the ribbed bogs or fens in which a pattern of narrow (2- to 3-m wide), low (<1 m deep) ridges are oriented at right angles to the direction of the drainage (National Wetlands Working Group 1988). Wet pools or depressions occur between the ridges. These patterned peatlands may include string bog, Atlantic ribbed fen, or northern ribbed fen (National Wetlands Working Group 1988). They develop almost entirely north of 46°N latitude in east-central Canada and the adjacent U.S. They are minerotrophic peatlands in which the vegetation has developed into a pattern of strings (raised, usually linear features) and flarks (wet depressions separating the strings). The substrate chemistry is entirely acidic in some peatlands; in others, where bedrock or other substrate influence creates circumneutral to calcareous conditions, peatland chemistry may be entirely calcareous or vary from acidic to calcareous within the same peatland. In acidic portions, typical bog heaths predominate mixed with sedges. Dasiphora fruticosa ssp. floribunda is diagnostic of circumneutral to calcareous conditions. These peatlands usually develop in open basins and flat plains, and the patterned portion may occupy only a fraction of the entire peatland. The edge of the basin may be shallow to deep peat over a sloping substrate, where seepage waters provide nutrients.
Floristics: This group contains a moss peat with depths exceeding 40 cm. Dwarf-shrubs and thin-leaved graminoids are >25%, and trees <25%. There is a discontinuous to absent layer of Sphagnum peatmoss, with brown mosses (Calliergon, Campylium, Drepanocladus, Tomentypnum) present to dominant. Ericaceous dwarf-shrubs (especially Chamaedaphne calyculata but occasionally Andromeda polifolia, Kalmia polifolia, Vaccinium oxycoccos) may be common to minimal, with broad-leaved shrubs (Alnus incana, Betula glandulosa, Betula michauxii, Betula pumila, Dasiphora fruticosa ssp. floribunda, Myrica gale, Salix spp.) minor to dominant. Thin-leaved graminoids include Carex interior, Carex lasiocarpa, Carex limosa, Carex livida, Eriophorum viridicarinatum, Muhlenbergia glomerata, Rhynchospora alba, and Trichophorum alpinum. Mosses include Aulacomnium palustre, Campylium stellatum, Limprichtia revolvens (= Drepanocladus revolvens), Pleurozium schreberi, Scorpidium scorpioides, Sphagnum angustifolium, Sphagnum capillifolium, Sphagnum magellanicum, and Tomentypnum nitens (Harris et al. 1996, Minnesota DNR 2003).
Dynamics: No Data Available
Environmental Description: Soil/substrate/hydrology: These fens develop in open basins where lateral groundwater flow through circumneutral to calcareous parent materials creates moderately to strongly alkaline conditions. They are found on level to gently sloping surfaces, or in closed wet depressions (sometimes as floating mats), and along wetland margins and lake- and rivershores The shore fens are occasionally flooded, and so are included here because flooding tends to create moderately alkaline conditions.
Geographic Range: This group is found across the boreal regions of eastern North America, primarily in Canada, but potentially in subboreal parts of the Laurentian-Acadian region of the United States.
Nations: CA,US
States/Provinces: MB, ME, MI, MN, NB, NH?, NS, NY?, ON, QC, WI
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.948485
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: GNR
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 2 Shrub & Herb Vegetation Class | C02 | 2 |
Subclass | 2.C Shrub & Herb Wetland Subclass | S44 | 2.C |
Formation | 2.C.2 Temperate to Polar Bog & Fen Formation | F016 | 2.C.2 |
Division | 2.C.2.Na North American Bog & Fen Division | D029 | 2.C.2.Na |
Macrogroup | 2.C.2.Na.2 Shrubby cinquefoil - Woolly-fruit Sedge / Star Campylium Moss Alkaline Fen Macrogroup | M877 | 2.C.2.Na.2 |
Group | 2.C.2.Na.2.e Shrubby-cinquefoil - Woolly-fruit Sedge Eastern Boreal Alkaline Fen Group | G804 | 2.C.2.Na.2.e |
Alliance | A4400 Smooth Sawgrass - Needle Beaksedge - <i>Solidago ohioensis</i> Shore Fen Alliance | A4400 | 2.C.2.Na.2.e |
Alliance | A4401 <i>Chamaedaphne calyculata - Myrica gale</i> / Woolly-fruit Sedge Fen Alliance | A4401 | 2.C.2.Na.2.e |
Alliance | A4441 Bog Birch / <i>Carex lasiocarpa - Carex flava</i> Alkaline Fen Alliance | A4441 | 2.C.2.Na.2.e |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: No Data Available
- Davis, R. G., and D. S. Anderson. 2001. Classification and distribution of freshwater peatlands in Maine. Northeastern Naturalist 8:1-50.
- Faber-Langendoen, D., J. Drake, S. Gawler, M. Hall, C. Josse, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, L. Sneddon, K. Schulz, J. Teague, M. Russo, K. Snow, and P. Comer, editors. 2010-2019a. Divisions, Macrogroups and Groups for the Revised U.S. National Vegetation Classification. NatureServe, Arlington, VA. plus appendices. [in preparation]
- Glaser, P. H. 1992a. Raised bogs in eastern North America - regional controls for species richness and floristic assemblages. Journal of Ecology 80:535-554.
- Harris, A. G., S. C. McMurray, P. W. C. Uhlig, J. K. Jeglum, R. F. Foster, and G. D. Racey. 1996. Field guide to the wetland ecosystem classification for northwestern Ontario. Ontario Ministry of Natural Resources, Northwest Science and Technology, Thunder Bay, Ontario. Field guide FG-01. 74 pp. plus appendix.
- Kost, M. A., D. A. Albert, J. G. Cohen, B. S. Slaughter, R. K. Schillo, C. R. Weber, and K. A. Chapman. 2007. Natural communities of Michigan: Classification and description. Report No. 2007-21, Michigan Natural Features Inventory, Lansing. 314 pp. [http://web4.msue.msu.edu/mnfi/reports/2007-21_Natural_Communites_of_Michigan_Classification_and_Description.pdf]
- Minnesota DNR [Minnesota Department of Natural Resources]. 2003. Field guide to the native plant communities of Minnesota: The Laurentian Mixed Forest Province. Ecological Land Classification Program, Minnesota County Biological Survey, and Natural Heritage and Nongame Research Program. Minnesota Department of Natural Resources, St. Paul.
- National Wetlands Working Group. 1988. Wetlands of Canada. Ecological Land Classification Series, No. 24. Sustainable Development Branch, Environment Canada, Ottawa, Ontario, and Polyscience Publications Inc., Montreal, Quebec. 452 pp.