Print Report

CEGL002623 Schoenoplectus tabernaemontani Temperate Marsh

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Softstem Bulrush Temperate Marsh

Colloquial Name: No Data Available

Hierarchy Level:  Association

Type Concept: This relatively widespread wetland occurs on pond and lake margins, and in backwater areas. It also occupies basins where the water table may remain relatively high, but which can drop below the soil surface late in the growing season. Elevations range from sea level in coastal areas to 2045 m (6700 feet) in the Rocky Mountains. Stands are flooded for most or all of the growing season. Stands can have water from 0 (exposed soil) to approximately 1.5 m deep, but usually are less than 1 m. Within a stand, water levels can vary by up to 1 m during the year. The water can be fresh to mildly saline. Soils are deep, poorly drained muck, peat, or mineral. This association is often a monotypic stand of Schoenoplectus tabernaemontani, but is also often mixed with one or two other Schoenoplectus species. This association is described as only those stands where Schoenoplectus tabernaemontani is the dominant bulrush. Schoenoplectus acutus may be present, but only in subdominant amounts. Other species are largely absent or present in limited amounts and include Carex aquatilis, Carex buxbaumii, Carex utriculata, Eleocharis palustris, Nuphar polysepala, Polygonum spp., Potamogeton spp., Mentha arvensis, and Galium triflorum. Adjacent deeper water sites are typically dominated by Typha latifolia, while drier sites support herbaceous communities dominated by Carex spp., Poa pratensis, or other grasses.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This association is defined as a PNV vegetation type. If it were renamed as a dominance type the species would include Schoenoplectus tabernaemontani and Carex aquatilis. This association is described as only those stands where Schoenoplectus tabernaemontani is the dominant bulrush. Schoenoplectus acutus may be present, but only in subdominant amounts. The Scirpus acutus Habitat Type (Hansen et al. 1995), Scirpus acutus community type (Kunze 1994), and Schoenoplectus acutus var. acutus - Schoenoplectus tabernaemontani (Kittel et al. 1999b) each describe an association where either of the two species can be dominant, either alone or in any combination. The California reference only refers to several Schoenoplectus species but never Schoenoplectus tabernaemontani.

Similar NVC Types: No Data Available
note: No Data Available

Physiognomy and Structure: No Data Available

Floristics: This association is often a monotypic stand of Schoenoplectus tabernaemontani, but is also often mixed with one or two other Schoenoplectus species. This association is described as only those stands where Schoenoplectus tabernaemontani (= Schoenoplectus validus; = Scirpus validus) is the dominant bulrush. Schoenoplectus acutus (= Scirpus acutus) may be present, but only in subdominant amounts. Other species are largely absent or present in limited amounts and include Carex aquatilis, Carex buxbaumii, Carex utriculata, Eleocharis palustris, Nuphar polysepala (= Nuphar lutea ssp. polysepala), Polygonum spp., Potamogeton spp., Mentha arvensis, and Galium triflorum.

Dynamics:  Schoenoplectus acutus and Schoenoplectus tabernaemontani are early colonizers of suitable habitats (Hansen et al. 1995) and are able to persist under wet conditions. Schoenoplectus spp. stands are generally considered permanent wetland communities. They will remain in place unless the hydrologic regime is severely altered. If water levels have fallen, stands can burn in either late fall or early spring. Stands of Schoenoplectus are important to wildlife species, especially birds, by providing cover and nesting habitat.

Environmental Description:  This relatively widespread wetland occurs on pond and lake margins, and in backwater areas. It also occupies basins where the water table may remain relatively high, but which can drop below the soil surface late in the growing season. Elevations range from sea level in coastal areas to 2025 m (0-6700 feet) in the Rocky Mountains. Stands are flooded for most or all of the growing season. Stands can have water from 0 (exposed soil) to approximately 1.5 m deep, but usually are less than 1 m. Within a stand, water levels can vary by up to 1 m during the year. The water can be fresh to mildly saline. Soils are deep, poorly drained muck, peat, or mineral. Adjacent deeper water sites are typically dominated by Typha latifolia, while drier sites support herbaceous communities dominated by Carex spp., Poa pratensis, or other grasses.

Geographic Range: This is a relatively widespread wetland association, reported from throughout the Pacific Northwest, and the interior regions of Montana and Wyoming, south into California and Colorado.

Nations: CA,US

States/Provinces:  AB, BC, CA, CO, ID, MT, OR, WA, WY




Confidence Level: High

Confidence Level Comments: No Data Available

Grank: G5

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: < Schoenoplectus acutus var. acutus - Schoenoplectus tabernaemontani (Kittel et al. 1999b) [Includes all combinations of Schoenoplectus acutus and Schoenoplectus tabernaemontani.]
= Schoenoplectus validus Association (Crowe et al. 2004)
< Scirpus acutus Habitat Type (Hansen et al. 1995) [Includes all combinations of Schoenoplectus acutus and Schoenoplectus tabernaemontani.]
< Scirpus acutus community type (Kunze 1994) [(p.24,81). Includes pure stands of Schoenoplectus tabernaemontani or Schoenoplectus acutus.]
= Scirpus validus Association (Kovalchik 1993) [(p.181)]
= Scirpus validus community type (Kunze 1994) [(p. 49)]

Concept Author(s): Western Ecology Group

Author of Description: Western Ecology Group

Acknowledgements: No Data Available

Version Date: 02-02-04

  • ANHIC [Alberta Natural Heritage Information Centre]. 2018. Community database files. Alberta Natural Heritage Information Centre, Parks and Protected Areas Division, Alberta Community Development, Edmonton.
  • Boss, T. R. 1983. Vegetation ecology and net primary productivity of selected freshwater wetlands in Oregon. Ph.D. dissertation, Oregon State University, Corvallis. 236 pp.
  • Bourgeron, P. S., and L. D. Engelking, editors. 1994. A preliminary vegetation classification of the western United States. Unpublished report. The Nature Conservancy, Western Heritage Task Force, Boulder, CO. 175 pp. plus appendix.
  • Crowe, E. A., B. L. Kovalchik, and M. J. Kerr. 2004. Riparian and wetland vegetation of central and eastern Oregon. Oregon Natural Heritage Information Center, Institute for Natural Resources, Oregon State University, Portland. 473 pp. [http://oregonstate.edu/ornhic/ publications.html]
  • Hansen, P. L., R. D. Pfister, K. Boggs, B. J. Cook, J. Joy, and D. K. Hinckley. 1995. Classification and management of Montana''s riparian and wetland sites. Miscellaneous Publication No. 54. Montana Forest and Conservation Experiment Station, School of Forestry, University of Montana. 646 pp. plus posters.
  • Hop, K., M. Reid, J. Dieck, S. Lubinski, and S. Cooper. 2007. U.S. Geological Survey-National Park Service Vegetation Mapping Program: Waterton-Glacier International Peace Park. U.S. Geological Survey, Upper Midwest Environmental Sciences Center, La Crosse, WI. 131 pp. plus Appendices A-L.
  • IDCDC [Idaho Conservation Data Center]. 2005. Wetland and riparian plant associations in Idaho. Idaho Conservation Data Center, Idaho Department of Fish and Game, Boise. [http://fishandgame.idaho.gov/tech/CDC/ecology/wetland_riparian_assoc.cfm] (accessed 14 June 2005).
  • Jankovsky-Jones, M., C. J. Murphy, and C. L. Coulter. 2001. Riparian and wetland plant associations of southwestern Idaho in the Lower Snake River District, Bureau of Land Management. Idaho Conservation Data Center, Idaho Department of Fish and Game, Boise.
  • Kagan, J. S., J. A. Christy, M. P. Murray, and J. A. Titus. 2004. Classification of native vegetation of Oregon. January 2004. Oregon Natural Heritage Information Center, Portland. 52 pp.
  • Kittel, G., E. Van Wie, M. Damm, R. Rondeau, S. Kettler, A. McMullen, and J. Sanderson. 1999b. A classification of riparian and wetland plant associations of Colorado: A user''s guide to the classification project. Colorado Natural Heritage Program, Colorado State University, Fort Collins CO. 70 pp. plus appendices.
  • Kovalchik, B. L. 1993. Riparian plant associations on the national forests of eastern Washington - Draft version 1. USDA Forest Service, Colville National Forest, Colville, WA. 203 pp.
  • Kovalchik, B. L. 2001. Classification and management of aquatic, riparian and wetland sites on the national forests of eastern Washington. Part 1: The series descriptions. 429 pp. plus appendix. [http://www.reo.gov/col/wetland_classification/wetland_classification.pdf]
  • Kunze, L. M. 1994. Preliminary classification of native, low elevation, freshwater wetland vegetation in western Washington. Washington State Department of Natural Resources, Natural Heritage Program. 120 pp.
  • MTNHP [Montana Natural Heritage Program]. 2002b. List of ecological communities for Montana. Montana Natural Heritage Program, Montana State Library, Helena, MT.
  • Reid, M. S., S. V. Cooper, and G. Kittel. 2004. Vegetation classification of Waterton-Glacier International Peace Park. Final report for USGS-NPS Vegetation Mapping Program, International Peace Park Mapping Project. NatureServe, Arlington VA.
  • Sanville, W. D., H. P. Eilers, T. R. Boss, and T. G. Pfleeger. 1986. Environmental gradients in northwest freshwater wetlands. Environmental Management 10:125-134.
  • Smith, S., and S. Smith. 1976. Vegetative types and landform classes. Pages 40-268 in: J. Tabor, editor. Inventory of riparian habitats and associated wildlife along the Columbia River. Final report prepared for Oregon State University Cooperative Wildlife Research Unit, Corvallis. 771 pp.
  • Thomas, D. W. 1980. Study of the intertidal vegetation of the Columbia River estuary, July-September 1980. Columbia River Estuary Study Task Force, Astoria, OR. 22 pp.
  • Viereck, L. A., C. T. Dyrness, A. R. Batten, and K. J. Wenzlick. 1992. The Alaska vegetation classification. General Technical Report PNW-GTR286. USDA Forest Service, Pacific Northwest Research Station, Portland, OR. 278 pp.
  • WNDD [Wyoming Natural Diversity Database]. No date. Unpublished data on file. Wyoming Natural Diversity Database, University of Wyoming, Laramie, WY.
  • WNHP [Washington Natural Heritage Program]. 2018. Unpublished data files. Washington Natural Heritage Program, Department of Natural Resources, Olympia, WA.
  • Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.