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D065 Ruppia spp. - Zannichellia palustris - Stuckenia pectinata Temperate Estuarine & Inland Brackish Aquatic Vegetation Division

Type Concept Sentence: This division is comprised of stands (beds) of submerged aquatic vascular plants in temperate coastal estuaries that have oligohaline to mesohaline water chemistry and continental interior waterbodies that have oligohaline to hypersaline chemistry, with a predominance of the taxa Ruppia maritima, Ruppia cirrhosa, Stuckenia pectinata, Zannichellia palustris, and Potamogeton perfoliatus, over that of either characteristically freshwater (low salt tolerance) or polyhaline vascular taxa.


Common (Translated Scientific) Name: Widgeonweed species - Horned Pondweed - Sago Pondweed Temperate Estuarine & Inland Brackish Aquatic Vegetation Division

Colloquial Name: Temperate Estuarine & Inland Brackish Aquatic Vegetation

Hierarchy Level:  Division

Type Concept: This division is comprised of stands (beds) of submerged aquatic vascular plants in temperate coastal estuaries that have oligohaline to mesohaline water chemistry and continental interior waterbodies that have oligohaline to hypersaline chemistry. The vegetation is composed of submerged hydromorphic herbaceous plants that can include both "meadow-forming" (e.g., Ruppia maritima, Stuckenia pectinata) and/or "canopy-forming" (e.g., Zannichellia palustris, Potamogeton perfoliatus) species and annual (e.g., Zannichellia palustris) and/or perennial species. Characteristic taxa include Ruppia maritima (primarily in coastal estuarine settings), Ruppia cirrhosa (primarily in inland settings), Zannichellia palustris, Stuckenia pectinata, and/or Potamogeton perfoliatus. Some freshwater species (e.g., Ceratophyllum spp., Elodea canadensis, Elodea nuttallii, Myriophyllum spicatum, Najas spp., Potamogeton spp., and Vallisneria americana) may be present, usually as minor associates.

Diagnostic Characteristics: This division is comprised of stands (beds) of submerged aquatic vascular plants in temperate coastal estuaries and interior waterbodies with oligohaline to mesohaline water chemistry, with a predominance of the taxa Ruppia maritima, Ruppia cirrhosa, Stuckenia pectinata, Zannichellia palustris, and Potamogeton perfoliatus, over freshwater (low salt tolerance) or polyhaline vascular taxa.

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: Due to its cosmopolitan distribution and wide salinity tolerance, Ruppia maritima may occur in monospecific vascular stands that can be assigned to one of three different divisions [see Similar NVC Types]. The extension of this division to continents other than North America needs review in the context of more information from those areas. The extension of this division to temperate and subtropical Eurasia, Africa, South America, and Australia is based on the occurrence of the primary North American species into those continents (Haynes 2000, Haynes and Hellquist 2000a, 2000b, Ito et al. 2010) and needs review in the context of information from those areas. For consistency with divisional distribution criteria for other units within USNVC Class 5 (Aquatic Vegetation) and due to a current lack of information about floristic patterns in the tropical settings, this division does not include tropical areas.

It is possible that this division might be better treated as individual macrogroups within 5.A.3.We ~Temperate Seagrass Aquatic Vegetation Division (D064)$$ and 5.A.3.Xd ~Tropical Saltwater Vegetation Division (D063)$$, subdividing the Ruppia maritima stands based on associated species (though monodominant stands may need to be separated based on ecological and geographic location).

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

Physiognomy and Structure: The vegetation is composed of submerged hydromorphic herbaceous plants that can include both "meadow-forming" (e.g., Ruppia maritima, Stuckenia pectinata) and/or "canopy-forming" (e.g., Zannichellia palustris, Potamogeton perfoliatus) species (Batiuk et al. 1992) and annual (e.g., Zannichellia palustris) and/or perennial species.

Floristics: Characteristic taxa include Ruppia maritima (primarily in coastal estuarine settings), Ruppia cirrhosa (primarily in inland settings), Zannichellia palustris, Stuckenia pectinata (= Potamogeton pectinatus), and/or Potamogeton perfoliatus. Some freshwater species (e.g., Ceratophyllum spp., Elodea canadensis, Elodea nuttallii, Myriophyllum spicatum, Najas spp., Potamogeton spp., and Vallisneria americana) may be present, usually as minor associates.

Dynamics:  No Data Available

Environmental Description:  Stands occur in intertidal and subtidal areas of estuaries along the ocean coasts or in semipermanently to permanently flooded areas of inland saline marshes and creeks (these inland areas are primarily in arid areas of western North America). The minimal depth limits of the beds are determined by low or high tide levels and the maximum depth limits by the penetration of light sufficient for photosynthesis, the latter being a function of water depth and water clarity. Kanrud (1991) identified maximum depth at 4 m. Beds generally occur in areas with moderate current velocities (<-50 cm/sec in Chesapeake Bay (Koch et al. 2000)) and, usually, moderate wave action. Koch et al. (2000) noted that the "canopy-forming" Zannichellia palustris was more limited by wave action than the "meadow-forming" Stuckenia pectinata (Ruppia maritima is a meadow-forming species, but its flowering/fruiting structures are wave sensitive). Water salinity in coastal areas ranges from oligohaline to mesohaline. In the Chesapeake Bay of Maryland and Virginia, stands that can be assigned to this division (Ruppia and Potamogeton Communities of Moore et al. (2000)) occupy areas that experience average spring salinities of 1-11 practical salinity units (psu) and average autumn salinities of 6-18 psu (Schubel and Pritchard 1987, Moore et al. 2000). Water chemistry in inland stands and in isolated lagoons and pools may be hypersaline (Ito et al. 2010).

Climate: Climate spans a wide range, from subtropical to sub-boreal and from humid to arid. Stands are found from slightly below sea level along the coasts to at least 2800 m (9100 feet) in Colorado.

Soils/substrate: Substrates are muddy to sandy. Through literature review, Koch et al. (2000) concluded that mixtures of Ruppia maritima, Vallisneria americana, Stuckenia pectinata, and Potamogeton perfoliatus persisted on substrates consisting of from 5-90% fine materials (<63 mm) and that the latter two species could be found on silty substrates. Overly fine substrates as less likely to support healthy beds because of decreased pore water exchange with the overlying water column and greater potential for sulfide accumulations; overly coarse sediments have lower nutrient content (Koch et al. 2000). Generally, substrates have less than 5% organic matter content (Koch et al. 2000).

Biogeography: This vegetation is found throughout most biotic regions of temperate North America. The vascular plant floristic composition is relatively uniform throughout and, within its geographic range, its occurrence appears to be more a result of water chemistry conditions than of climate.

Geographic Range: This vegetation is found throughout the oligohaline to mesohaline estuarine zones of both the Atlantic/Gulf and Pacific coasts of temperate North America. Its range in the interior is less well known, but probably includes at least most of the Great Plains and arid interior western North America.

Nations: AU,CA,MX,US

States/Provinces:  AL, AZ?, CA, CO, CT, DE, FL, GA, HI?, LA, MA, MD, ME, MS, MT?, NC, ND?, NE?, NH, NJ, NM?, NV?, NY, OK?, OR?, RI, SC?, SD?, TX, UT?, VA, WA?, WY?




Confidence Level: Low

Confidence Level Comments: No Data Available

Grank: GNR

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: >< Ruppia Community + Potamogeton Community (Moore et al. 2000)
= Brackish Subtidal Aquatic Bed (Reschke 1990)

Concept Author(s): K.A. Moore, D.J. Wilcox, and R.J. Orth (2000)

Author of Description: C. Lea

Acknowledgements: No Data Available

Version Date: 10-29-15

  • Batiuk, R., R. Orth, K. Moore, J. C. Stevenson, W. Dennison, L. Staver, V. Carter, N. Rybicki, R. Hickman, S. Kollar, and S. Bieber. 1992. Submerged aquatic vegetation habitat requirements and restoration targets: A technical synthesis. Report for the Chesapeake Bay Program CBP/TRS 245/00 EPA 903-R-00-014. CBP/TRS-83/92. Annapolis, MD.
  • 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]
  • Haynes, R. R. 2000. Ruppiaceae. Pages 75-76 in: Flora of North America Editorial Committee, editors. Flora of North America north of Mexico. Volume 22. Oxford University Press, New York, NY.
  • Haynes, R. R., and C. B. Hellquist. 2000a. Potamogetonaceae. Pages 47-74 in: Flora of North America Editorial Committee, editors. Flora of North America north of Mexico. Volume 22. Oxford University Press, New York, NY.
  • Haynes, R. R., and C. B. Hellquist. 2000b. Zannichelliaceae. Pages 84-85 in: Flora of North America Editorial Committee, editors. Flora of North America north of Mexico. Volume 22. Oxford University Press, New York, NY.
  • Ito, Y., T. Ohi-Toma, J., Murata, and N. Tanaka. 2010. Hybridization and polyploidy of an aquatic plant, Ruppia (Ruppiaceae), inferred from plastid and nuclear DNA phylogenies. American Journal of Botany 97:1156-1167. [http://www.amjbot.org/content/97/7/1156.full.pdf+html]
  • Kanrud, H. A. 1991. Wigeongrass (Ruppia maritima L.): A literature review. USDI Fish and Wildlife Service, Fish and Wildlife Research 10. Jamestown, ND.
  • Koch, E. W., S. Ailstock, and J. C. Stevenson. 2000. Beyond light: Physical, geological and chemical habitat requirements. In: R. A. Batiuk, P. Bergstrom, M. Kemp, E. W. Koch, L. Murray, J. C. Stevenson, R. Bartleson, V. Carter, N. B. Rybicki, J. M. Landwehr, C. L. Gallegos, L. Karrh, M. Naylor, D. Wilcox, K. A. Moore, S. Ailstock, and M. Teichberg. Chesapeake Bay submerged aquatic vegetation water quality and habitat-based requirements and restoration targets: A second technical synthesis. Report for the Chesapeake Bay Program CBP/TRS 245/00 EPA 903-R-00-014. U.S. Environmental Protection Agency, Annapolis, MD.
  • Moore, K. A., D. J. Wilcox, and R. J. Orth. 2000. Analysis of the abundance of submersed aquatic vegetation communities in the Chesapeake Bay. Estuaries 23:115-127.
  • Reschke, C. 1990. Ecological communities of New York State. New York Natural Heritage Program, New York State Department of Environmental Conservation, Latham, NY. 96 pp.
  • Schubel, J. R., and D. W. Pritchard. 1987. A brief physical description of Chesapeake Bay. Pages 1-32 in: S. K. Majumdar, L. W. Hall, Jr., and H. M. Austin, editors. Contaminant Problems and Management of Living Chesapeake Bay Resources. A publication of the Pennsylvania Academy of Science. Typehouse of Easton, Philipsburg, NJ.