Print Report
G123 Salicornia spp. - Sarcocornia spp. - Spartina spartinae Tidal Flat & Panne Group
Type Concept Sentence: These are tidally-influenced hypersaline areas found along the Atlantic and Gulf of Mexico coasts from the New England states and the Canadian Maritime Provinces south to northern Mexico, dominated by Salicornia spp. and Sarcocornia spp., as well as Batis maritima, Distichlis spicata, Spartina alterniflora, Spartina spartinae, and/or Sporobolus virginicus.
Common (Translated Scientific) Name: Saltwort species - Swampfire species - Gulf Cordgrass Tidal Flat & Panne Group
Colloquial Name: Atlantic & Gulf Coastal Tidal Flat & Panne
Hierarchy Level: Group
Type Concept: Vegetation of this group occupies tidally-influenced hypersaline areas along the Atlantic Coast and Gulf of Mexico region from the New England states and the Canadian Maritime Provinces, along the southeastern coast and south to northern Mexico. Examples of this vegetation may occur in patches throughout this relatively large range. The southern limit depends on where the temperate-tropical line is set in relation to this division. These irregularly tidally-flooded marshes are generally somewhat hypersaline from evaporation of seawater after storm surges or exceptionally high tides. They vary somewhat locally in expression, but all tend to exhibit low vascular plant diversity, dominated by halophytic species. There are relatively few plant species which are able to occupy these environments. These include various species of the succulent genera Salicornia spp. and Sarcocornia spp., as well as several grasses (which may be stunted), including Distichlis spicata, Spartina alterniflora, Spartina spartinae, and/or Sporobolus virginicus. Some more southerly associations may contain or be dominated by Batis maritima. Common associates include Atriplex spp., Limonium carolinianum, Monanthochloe littoralis, Plantago maritima var. juncoides, Suaeda maritima, and Triglochin maritima. Total vegetative cover is quite variable, from near total absence of vascular plants to a dense cover of vascular and nonvascular plants; however, unlike high marsh Spartina vegetation, pannes do not feature dense Spartina cover. Algal mats are characteristically present, visible even in densely vegetated pannes. In some cases, blue-green algae may contribute significantly more biomass than vascular species.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: Salt marsh zonation has long been recognized and well-studied. The four groups in ~North American Atlantic & Gulf Coastal Salt Marsh Macrogroup (M079)$$ reflect these common salt marsh zones (low marsh, high marsh, brackish marsh, panne); see, for example, Adam (1990) and Mendelssohn and McKee (2000). This type description fits Atlantic Canada. Salt pannes there usually include Triglochin maritima, Glaux maritima, and Plantago maritima. In western Nova Scotia, they include Agalinis maritima (a coastal plain species).
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: These pannes are typically dominated by low, salt-tolerant forbs, with variable cover, and they typically occur as islands within other marsh vegetation. Stunted saltmarsh grasses may be present.
Floristics: There are relatively few plant species which are able to occupy these environments. These include various species of the succulent genera Salicornia (e.g., Salicornia depressa (= Salicornia virginica), Salicornia bigelovii, Salicornia maritima) and Sarcocornia (e.g., Sarcocornia pacifica), as well as several grasses (which may be stunted), including Distichlis spicata, Spartina alterniflora, Spartina spartinae, and/or Sporobolus virginicus. Some more southerly associations may contain or be dominated by Batis maritima. Other common associates include Agalinis maritima, Atriplex spp., Blutaparon vermiculare, Cynanchum angustifolium, Limonium carolinianum, Lycium carolinianum, Monanthochloe littoralis, Plantago maritima var. juncoides, Sesuvium portulacastrum, Suaeda maritima, Symphyotrichum tenuifolium (= Aster tenuifolius), and Triglochin maritima. Scattered individuals of Avicennia germinans can occur in Florida and southern Texas. Total vegetative cover is quite variable, from near total absence of vascular plants to a dense cover of vascular and nonvascular plants. Algal mats are characteristically present, visible even in densely vegetated pannes. Blue-green algae are an important component of these mats, in some cases contributing significantly more biomass to the community than do vascular species. The following algae were noted to occur in association with Spartina alterniflora in the littoral zone of a Massachusetts salt marsh: Hydrocoleum lyngbyaceum, Lyngbea spp., Microcoleus chthonoplastes, Nodularia harveyana, Oscillatoria amphibia, Oscillatoria subuliformis, and Symploca spp. (Webber 1967). In Atlantic Canada, in addition to the above species, salt pannes may include Glaux maritima, and in western Nova Scotia, they include Agalinis maritima (a coastal plain species) (S. Basquill pers. comm. 2015).
Dynamics: Salt pannes are part of the shifting mosaic of plant communities of the salt marsh complex. They tend to occur more frequently on the high marsh, but are present in the low marsh as well. Pannes are variable in shape and likely variable in origin. Formation can result from ice-scouring or rafting flotsam that scrapes away or smothers existing vegetation, or from peat compaction, mosquito ditch levees, or tidal creekbank erosion that blocks or impedes drainage. Lack of vegetation decreases local sedimentation, which also maintains lower micro-relief (Redfield 1972). Evaporation from these poorly drained shallow depressions leads to hypersaline conditions (Niering and Warren 1980, Bertness et al. 1992). Gradients of salinity and standing water depth and duration correlate to vegetative cover and composition. The lowest portions of pannes tend to be wetter and more saline and can have little or no vegetation. As duration of wetness and salinity decrease across the micro-relief, forb-dominated species assemblages tend to dominate followed by mixed graminoid-forb assemblages at the outer, higher edges (Redfield 1972). Pannes can be ephemeral features on the marsh, and vegetation cover and composition can vary from year to year. Unvegetated, soft-bottomed pannes generally have plentiful worm and crab burrows (Godfrey et al. 1978).
Environmental Description: Vegetation of this association tends to develop in shallow depressions in salt marshes where drainage is poor. They tend to occur more frequently on the high marsh but occur within low marsh as well. Pannes form in depressions that range from 2-30 cm lower than the elevation of the marsh. The depressions are regularly to irregularly flooded by tides, and as the water evaporates during low tide, the salinity concentration increases, forming "salt pannes." Substrate is soft, silty muck or peat of variable density.
Geographic Range: This hypersaline vegetation is found along the Atlantic Coast and Gulf of Mexico region from the New England states and the southern Maritime Provinces of Canada south to northern Mexico. The southern limit depends on where the temperate-tropical line is set in relation to this division.
Nations: CA,MX,US
States/Provinces: AL, CT, DE, FL, GA, LA, MA, MD, ME, MS, MXTAM, NB, NC, NH, NJ, NS, NY, QC, RI, SC, TX, VA
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.837392
Confidence Level: Low
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.5 Salt Marsh Formation | F035 | 2.C.5 |
Division | 2.C.5.Nb North American Atlantic & Gulf Coastal Salt Marsh Division | D034 | 2.C.5.Nb |
Macrogroup | 2.C.5.Nb.1 North American Atlantic & Gulf Coastal Salt Marsh Macrogroup | M079 | 2.C.5.Nb.1 |
Group | 2.C.5.Nb.1.b Saltwort species - Swampfire species - Gulf Cordgrass Tidal Flat & Panne Group | G123 | 2.C.5.Nb.1.b |
Alliance | A3955 Turtleweed - Swampfire species - Saltwort species Intertidal Salt Flat Alliance | A3955 | 2.C.5.Nb.1.b |
Alliance | A3956 Saltgrass - Seashore Dropseed Intertidal Salt Marsh Alliance | A3956 | 2.C.5.Nb.1.b |
Alliance | A3957 Gulf Cordgrass - Seashore Dropseed - Shoregrass Intertidal Salt Marsh Alliance | A3957 | 2.C.5.Nb.1.b |
Alliance | A4487 <i>Salicornia depressa - Salicornia maritima</i> Intertidal Salt Flat Alliance | A4487 | 2.C.5.Nb.1.b |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: = Salicornia - Bassia salt flat (Harvill 1965) [Virginia]
= Salicornia tidal flat (Clovis 1968) [Virginia]
= Salicornietum ambiguae (Conard 1935) [New York]
= Sarcocornia perennis - (Distichlis spicata, Spartina alterniflora) Dwarf-shrubland (Bartgis 1986)
= Spartina alterniflora / Salicornia europaea community [Salt panne] (Clancy 1993b) [Delaware]
>< Glasswort-Saltwort Series (Diamond 1993)
= Pan (Nichols 1920) [Connecticut]
= Panne (Good 1965) [New Jersey]
= Panne marsh (Baumann 1978b) [Virginia]
= Pans (Higgins et al. 1971) [Assateague Island]
= Pans (Hill 1986) [Assateague Island]
? Salt Marsh (Rawinski 1984a) [formerly Southern New England and Gulf of Maine Salt Marshes]
= Salt marsh complex, pannes (Breden 1989) [New Jersey]
= Salt pan (Klotz 1986) [Virginia]
= Salt panne (Miller and Egler 1950) [Connecticut]
= Salt panne (Reschke 1990) [New York]
= Stunted Spartina alterniflora community (Miller and Egler 1950) [Connecticut]
= Salicornia tidal flat (Clovis 1968) [Virginia]
= Salicornietum ambiguae (Conard 1935) [New York]
= Sarcocornia perennis - (Distichlis spicata, Spartina alterniflora) Dwarf-shrubland (Bartgis 1986)
= Spartina alterniflora / Salicornia europaea community [Salt panne] (Clancy 1993b) [Delaware]
>< Glasswort-Saltwort Series (Diamond 1993)
= Pan (Nichols 1920) [Connecticut]
= Panne (Good 1965) [New Jersey]
= Panne marsh (Baumann 1978b) [Virginia]
= Pans (Higgins et al. 1971) [Assateague Island]
= Pans (Hill 1986) [Assateague Island]
? Salt Marsh (Rawinski 1984a) [formerly Southern New England and Gulf of Maine Salt Marshes]
= Salt marsh complex, pannes (Breden 1989) [New Jersey]
= Salt pan (Klotz 1986) [Virginia]
= Salt panne (Miller and Egler 1950) [Connecticut]
= Salt panne (Reschke 1990) [New York]
= Stunted Spartina alterniflora community (Miller and Egler 1950) [Connecticut]
- Adam, P. 1990. Saltmarsh Ecology. Cambridge University Press, Cambridge. 461 pp.
- Bartgis, R. 1986. Natural community descriptions. Unpublished draft. Maryland Natural Heritage Program, Maryland Department of Natural Resources, Annapolis.
- Baumann, C. 1978b. The effects of overwash on the vegetation of a Virginia barrier island. M.A. thesis. College of William and Mary, Williamsburg, VA. 104 pp.
- Bertness, M. D., L. Gough, and S. W. Shumway. 1992. Salt tolerances and the distribution of fugitive salt marsh plants. Ecology 73(5):1842-1851.
- Breden, T. F. 1989. A preliminary natural community classification for New Jersey. Pages 157-191 in: E. F. Karlin, editor. New Jersey''s rare and endangered plants and animals. Institute for Environmental Studies, Ramapo College, Mahwah, NJ. 280 pp.
- Clancy, K. 1993b. A preliminary classification of the natural communities of Delaware. Unpublished draft. Delaware Natural Heritage Inventory, Division of Parks and Recreation, Dover. 30 pp.
- Clovis, J. F. 1968. The vegetation of Smith Island, Virginia. Castanea 33:115-121.
- Conard, H. S. 1935. The plant associations of central Long Island. The American Midland Naturalist 16:433-516.
- Diamond, D. D. 1993. Classification of the plant communities of Texas (series level). Unpublished document. Texas Natural Heritage Program, Austin. 25 pp.
- FNA Editorial Committee [Flora of North America Editorial Committee], editors. 2003. Flora of North America, north of Mexico. Volume 4. Magnoliophyta: Caryophyllidae, part 1. Oxford University Press, New York. 559 pp.
- 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]
- Godfrey, P. J., M. Benedict, and M. Soukup. 1978. A guide to the ecology of Cape Cod National Seashore (Mary 1978 draft). National Park Service Cooperative Research Unit, Institute for Man and Environment, University of Massachusetts, Amherst.
- Good, R. E. 1965. Salt marsh vegetation, Cape May, New Jersey. Bulletin of the New Jersey Academy of Science 10:1-11.
- Harvill, A. M., Jr. 1965. The vegetation of Parramore Island, Virginia. Castanea 30:226-228.
- Higgins, E. A. T., R. D. Rappleye, and R. G. Brown. 1971. The flora and ecology of Assateague Island. University of Maryland Experiment Station Bulletin A-172. 70 pp.
- Hill, S. R. 1986. An annotated checklist of the vascular flora of Assateague Island (Maryland and Virginia). Castanea 5:265-305.
- Kartesz, J. T. 1999. A synonymized checklist and atlas with biological attributes for the vascular flora of the United States, Canada, and Greenland. First edition. In: J. T. Kartesz and C. A. Meacham. Synthesis of the North American Flora, Version 1.0. North Carolina Botanical Garden, Chapel Hill, NC.
- Klotz, L. H. 1986. The vascular flora of Wallops Island and Wallops Mainland, Virginia. Castanea 51:306-326.
- Mendelssohn, I. A., and K. L. McKee. 2000. Saltmarshes and mangroves. Pages 501-536 in: M. G. Barbour and W. D. Billings, editors. North American terrestrial vegetation. Second edition. Cambridge University Press, New York. 434 pp.
- Metzler, K. J., and J. Barrett. 1992. Connecticut community classification. Unpublished draft. Connecticut Department of Environmental Protection, Natural Resources Center, Natural Diversity Database, Hartford.
- Miller, W. R., and F. E. Egler. 1950. Vegetation of the Wequetequock-Pawcatuck tidal-marshes, Connecticut. Ecological Monographs 20:143-172.
- Nelson, J. B. 1986. The natural communities of South Carolina: Initial classification and description. South Carolina Wildlife and Marine Resources Department, Division of Wildlife and Freshwater Fisheries, Columbia, SC. 55 pp.
- Nichols, G. E. 1920. The vegetation of Connecticut: III. The associations of depositing areas along the seacoast. Bulletin of the Torrey Botanical Club 47:511-548.
- Niering, W. A., and R. S. Warren. 1980. Vegetation patterns and processes in New England salt marshes. BioScience 30:301-307.
- Rawinski, T. 1984a. Natural community description abstract - southern New England calcareous seepage swamp. Unpublished report. The Nature Conservancy, Boston, MA. 6 pp.
- Redfield, A. C. 1972. Development of a New England salt marsh. Ecological Monographs 42(2):201-237.
- 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.
- Schafale, M. P., and A. S. Weakley. 1990. Classification of the natural communities of North Carolina. Third approximation. North Carolina Department of Environment, Health, and Natural Resources, Division of Parks and Recreation, Natural Heritage Program, Raleigh. 325 pp.
- Swain, P. C., and J. B. Kearsley. 2001. Classification of natural communities of Massachusetts. September 2001 draft. Natural Heritage and Endangered Species Program, Massachusetts Division of Fisheries and Wildlife, Westborough, MA.
- Weakley, A. S. 2007. Flora of the Carolinas, Virginia, Georgia, and surrounding areas. Unpublished working draft of 11 January 2007. University of North Carolina Herbarium (NCU), North Carolina Botanical Garden, University of North Carolina, Chapel Hill. [http://www.herbarium.unc.edu/flora.htm]
- Webber, E. E. 1967. Bluegreen algae from a Massachusetts salt marsh. Bulletin of the Torrey Botanical Club 94:99-106.