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A3654 Spartina pectinata Wet Prairie Alliance

Type Concept Sentence: The vegetation of this alliance is characterized by dense stands of graminoids 1-2 m tall with scattered to very infrequent woody plants. Spartina pectinata and Calamagrostis canadensis are typically the two most common species with Spartina pectinata sometimes forming near monocultures. This alliance is found primarily in central North America. Stands of this wide-ranging alliance are found on level to gently sloping sites with sand, loam, or clay soils. All sites are typically flooded for part of the winter and spring and usually remain saturated for much of the growing season.


Common (Translated Scientific) Name: Prairie Cordgrass Wet Prairie Alliance

Colloquial Name: Prairie Cordgrass Wet Prairie

Hierarchy Level:  Alliance

Type Concept: The vegetation of this alliance is characterized by dense stands of graminoids 1-2 m tall with scattered to very infrequent woody plants. Spartina pectinata and Calamagrostis canadensis are typically the two most common species with Spartina pectinata sometimes forming near monocultures. Shrubs, particularly Salix discolor, Salix petiolaris, and Betula pumila, can be common in some stands in the northern part of this alliance''s range. Other common species are Carex aquatilis, Carex atherodes, Carex pellita, and Carex sartwellii. Species typical of mesic prairies can be present, including Andropogon gerardii, Muhlenbergia richardsonis, Panicum virgatum, and Sorghastrum nutans. Forbs can be abundant and include Helianthus grosseserratus, Lythrum alatum, Pycnanthemum virginianum, Symphyotrichum ericoides, Symphyotrichum novae-angliae, and Thalictrum dasycarpum. Shrubs and small trees are often present. Among these Cornus spp., Fraxinus pennsylvanica, and Salix spp. are typical. This alliance is found primarily in central North America. Stands of this wide-ranging alliance are found on level to gently sloping sites with sand, loam, or clay soils. They occur near lakes or rivers or in depressions. All sites are typically flooded for part of the winter and spring and usually remain saturated for much of the growing season.

Diagnostic Characteristics: Herbaceous wetlands in the midwestern U.S. and southern Ontario and Quebec dominated by Spartina pectinata possibly in conjunction with Calamagrostis canadensis.

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This alliance can grade into ~Athyrium filix-femina - Chamerion angustifolium ssp. angustifolium - Calamagrostis canadensis Meadow Alliance (A3946)$$. Calamagrostis canadensis is common in both.

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

Physiognomy and Structure: This alliance is characterized by the dominance of perennial graminoids, generally 1-2 m in height, and with high cover. Forbs are present in most stands, but generally with low abundance. Woody plants are scattered to very infrequent.

Floristics: The most abundant species are Calamagrostis canadensis, Carex aquatilis, Carex atherodes, Carex pellita (= Carex lanuginosa), Carex nebrascensis, Carex sartwellii, and Spartina pectinata. Other common graminoids include Andropogon gerardii, Muhlenbergia richardsonis, Panicum virgatum, Poa palustris (in the western part of this alliance''s range), and Sorghastrum nutans. In some stands, Spartina pectinata can form virtual monocultures, as a result of growth from vigorous rhizomes (Hansen et al. 1995, Johnson and Knapp 1995). Forbs can be abundant and include Glycyrrhiza lepidota, Helianthus grosseserratus, Lythrum alatum, Pycnanthemum virginianum, Symphyotrichum ericoides (= Aster ericoides), Symphyotrichum novae-angliae (= Aster novae-angliae), and Thalictrum dasycarpum. Shrubs and small trees are infrequent in the south and west but are often present in the north and east (Chapman 1984, MNNHP 1993). Among these Amorpha fruticosa, Cornus spp., Fraxinus pennsylvanica, and Salix spp., especially Salix petiolaris and Salix discolor, are typical.

Dynamics:  Spartina pectinata is an early colonizer of suitable habitat and is tolerant of sediment deposition (Weaver 1965, Hansen et al. 1995). On the South Platte River floodplain it appears to be an early colonizer of the fresh sediments laid down by the 1995 flood.

Stands of Spartina pectinata have high production rates; however, the rough-edged leaves make for poor forage quality, and it is not readily eaten by livestock or wildlife. Its tall height and thick growth provide shade and cover for wildlife and certain bird species (Hansen et al. 1988a).

Environmental Description:  This is a wide-ranging alliance found in the central United States. Locations supporting this alliance are moist, poorly drained, sometimes alkaline areas along ephemeral, intermittent or perennial streams, and overflow areas of large river floodplains. Weaver (1965) reported that, historically, large stands of Spartina pectinata occurred on mudflats of the Missouri River. This alliance can also be found in swales, meadows, and on the margins of marshes, ponds or lakes. Sites are generally level to gently sloping. Jones and Walford (1995) found stands along highly meandering, narrow (<12.5 m wide) floodplains, and often the channel was deeply entrenched. The water table is typically high, within 1 m of the surface; the sites are typically flooded for part of the winter and spring. Soils are fine-textured, ranging from clays to silt loam (Weaver 1960, Steinauer 1989), and may be slightly to moderately alkaline (Ungar 1974b, Hansen et al. 1995, Jones and Walford 1995). Soil water movement is rapid enough to preclude the accumulation of salts in the surface horizon. In the east, stands can experience droughty conditions in the summer and fall (Comer et al. 1995b), while in the southern and central portion of this alliance''s range they can remain saturated for much of the growing season (Küchler 1974).

Geographic Range: This alliance is found throughout the midwestern United States and adjacent southern Canada from Missouri and eastern Nebraska to Ohio and southern Ontario and Quebec.

Nations: CA,US

States/Provinces:  IA, IL, IN, KY?, MB, MI, MN, MO, ND, NE, OH, ON, QC, SD, WI




Confidence Level: Low

Confidence Level Comments: No Data Available

Grank: GNR

Greasons: No Data Available


Concept Lineage: This alliance contains the Midwestern portion of old A.1347.

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: = Spartina pectinata herbaceous alliance (Hoagland 1998a)

Concept Author(s): J. Drake, in Faber-Langendoen et al. (2013)

Author of Description: J. Drake

Acknowledgements: No Data Available

Version Date: 12-18-14

  • Chapman, K. A. 1984. An ecological investigation of native grassland in southern Lower Michigan. Unpublished Master''s thesis, Western Michigan University, Kalamazoo. 235 pp.
  • Comer, P. J., W. A. MacKinnon, M. L. Rabe, D. L. Cuthrell, M. R. Penskar, and D. A. Albert. 1995b. A survey of Lakeplain Prairie in Michigan. CZM Project 94D-0.04. Michigan Natural Features Inventory, Lansing, MI.
  • Faber-Langendoen, D., J. Drake, M. Hall, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, M. Russo, K. Schulz, L. Sneddon, K. Snow, and J. Teague. 2013-2019b. Screening alliances for induction into the U.S. National Vegetation Classification: Part 1 - Alliance concept review. NatureServe, Arlington, VA.
  • Faber-Langendoen, D., and Midwest State Natural Heritage Program Ecologists. 1996. Terrestrial vegetation of the midwest United States. International classification of ecological communities: Terrestrial vegetation of the United States. The Nature Conservancy, Arlington, VA.
  • 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.
  • Hansen, P., S. Chadde, R. Pfister, J. Joy, D. Svoboda, J. Pierce, and L. Myers. 1988a. Riparian site types, habitat types, and community types of southwestern Montana. Draft Version 1. University of Montana, Montana Riparian Association, School of Forestry, Missoula. 140 pp.
  • Hoagland, B. W. 1998a. Classification of Oklahoma vegetation types. Working draft. University of Oklahoma, Oklahoma Natural Heritage Inventory, Norman. 43 pp.
  • Johnson, S. R., and A. K. Knapp. 1995. The influence of fire on Spartina pectinata wetland communities in a northeastern Kansas tallgrass prairie. Canadian Journal of Botany 73:84-90.
  • Jones, G. P., and G. M. Walford. 1995. Major riparian vegetation types of eastern Wyoming. Submitted to Wyoming Department of Environmental Quality, Water Quality Division. Wyoming Natural Diversity Database, Laramie, WY. 245 pp.
  • MNNHP [Minnesota Natural Heritage Program]. 1993. Minnesota''s native vegetation: A key to natural communities. Version 1.5. Minnesota Department of Natural Resources, Natural Heritage Program, St. Paul, MN. 110 pp.
  • Steinauer, G. 1989. Characterization of the natural communities of Nebraska. Appendix D, pages 103-114 in: M. Clausen, M. Fritz, and G. Steinauer. The Nebraska Natural Heritage Program, two year progress report. Unpublished document. Nebraska Game and Parks Commission, Natural Heritage Program, Lincoln, NE.
  • Ungar, I. A. 1974b. The effect of soil factors on the distribution of halophytic species at South Park, Colorado. Bulletin of the Ecological Society of America 55(2):31-32 (Abstract).
  • Weaver, J. E. 1960. Flood plain vegetation of the central Missouri Valley and contacts of woodland with prairie. Ecological Monographs 30:37-64.
  • Weaver, J. E. 1965. Native vegetation of Nebraska. University of Nebraska Press, Lincoln. 185 pp.