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M057 Ammophila breviligulata - Uniola paniculata - Solidago sempervirens Dune & Grassland Macrogroup

Type Concept Sentence: This coastal grassland, shrubland and open vegetation type is found on well-drained to excessively drained sands on dunes and shorelines around the Great Lakes and Atlantic and Gulf coasts, as well as on rocky headlands in the North Atlantic.


Common (Translated Scientific) Name: American Beachgrass - Sea-oats - Seaside Goldenrod Dune & Grassland Macrogroup

Colloquial Name: Eastern North American Coastal Dune, Grassland & Rocky Headland

Hierarchy Level:  Macrogroup

Type Concept: This macrogroup encompasses coastal grasslands and shrublands along the Great Lakes, Lake Champlain, and Atlantic and Gulf coasts, occurring on sandy dunes and beaches along coastal shorelines and barrier islands, as well as on rocky headlands in the North Atlantic. It includes areas ranging from sparsely vegetated to lichen-dominated to grasslands and grassland-shrub complexes depending upon the degree of deposition, erosion, and distance from shore. Species composition varies geographically. Within the Great Lakes region and along the North Atlantic Coast, Ammophila breviligulata characterizes most herbaceous stands. Schizachyrium scoparium is common in many of these northern (not in Canada) sites as well. Common shrubs include Arctostaphylos uva-ursi, Hudsonia tomentosa, Juniperus communis, and Juniperus horizontalis. Some examples in the Great Lakes may also have a scattered overstory canopy dominated by Pinus banksiana, Pinus resinosa, and/or Pinus strobus, and on the Atlantic Coast, Pinus rigida or Pinus taeda. Along the Atlantic Coast Morella pensylvanica shrublands are common, and dwarf-shrubs include Empetrum nigrum or, less commonly, Corema. Solidago sempervirens is typical on Atlantic coastal sites. Uniola paniculata is diagnostic within sites along the South Atlantic Coast. Panicum amarum occurs on the foredunes, and Spartina patens and Schizachyrium littorale are common on the older dunes and sand flats. Soils are typically well-drained to excessively drained sands with little to no horizon development, or a thin patchy layer of organic material on rocky headlands. Heavy winds significantly impact these communities which can cause reworking of sand or by slower eolian processes. Sites along the Atlantic Coast are shaped by salt spray, overwash, and very high humidity. Fire suppression in the range of this macrogroup can cause an increase in woody species. Many areas have also been impacted by agriculture and grazing.

Diagnostic Characteristics: This vegetation is found on rocky headlands of the North Atlantic Coast, on coastal sandplains, and dynamic sandy dunes along and near shorelines of the Great Lakes, and Atlantic and Gulf coasts. Dunes are characterized by shifting sands and blowouts. The vegetation physiognomy ranges from sparsely vegetated to lichen-dominated to shrub-herb complexes and may contain a scattered coniferous overstory. Ammophila breviligulata is common in the Great Lakes and North Atlantic Coast examples and often occurs in conjunction with scattered low shrubs. Solidago sempervirens is characteristic on Atlantic coastal sites. In the South Atlantic and Gulf coasts, Uniola paniculata is the most common species.

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: It is not clear to what extent inland sandplains with dune-like characteristics fall here. The term "dune" could be generalized to be "shoreline." The extent of this type inward from the beach can be difficult to define, as dunes become more stable. Coastal grasslands, particularly on limestone, around the Great Lakes may fit here or in ~Laurentian-Acadian Calcareous Scrub & Grassland Macrogroup (M507)$$. Interdunal swales that have the diagnostic features of wetland types are excluded from this macrogroup. In the Canadian Maritimes, not all coastal headlands are rocky or even thin-soiled. In warmer areas, rock precludes tree development, hence the shrubland. In colder areas, trees (and in some cases taller shrubs) are excluded by harsh climatic influences. The soils/environmental setting of this type concept is heavily weighted to dune conditions (S. Basquill pers. comm. 2015).

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

Physiognomy and Structure: The cover and structure of vegetation are highly variable across the range of this macrogroup. It can range from sparsely to completely vegetated and include lichen-dominated, herb-dominated, shrub-herb complexes, and shrub-dominated areas. Some examples within the Great Lakes and North Atlantic Coast may contain a scattered coniferous overstory.

Floristics: This macrogroup includes a combination of grasslands, dwarf-shrublands, shrublands and open-treed savannas. On dunes along the Great Lakes and North Atlantic Coast, Ammophila breviligulata is the most common grass species (Leymus mollis may replace it northward in Newfoundland); Ammophila champlainensis is the most common grass on the shore of Lake Champlain. Other common species include Calamovilfa longifolia, Panicum spp., and Schizachyrium scoparium. In the Great Lakes, low evergreen shrubs such as Arctostaphylos uva-ursi, Juniperus communis, and Juniperus horizontalis occupy dune crests, dune fields, and also the ground layer in the savanna edge of dunes and sandplains. Prunus pumila, Salix cordata, and Salix myricoides (= Salix glaucophylloides) may occur, and Pinus banksiana, Pinus resinosa, Pinus strobus, and Thuja occidentalis often form a scattered overstory canopy. Coastal dunes of the Northeast are characterized by Carex silicea, Cenchrus tribuloides, Hudsonia tomentosa, Lathyrus japonicus, Morella pensylvanica, Panicum amarum, Panicum virgatum, Polygonella articulata, Schizachyrium littorale, Schizachyrium scoparium, and Solidago sempervirens.

Unusual expressions are sandplain grasslands and heathlands of the southern New England / New York coast. These are areas of graminoid- and shrub-dominated vegetation maintained by the combination of extreme conditions and periodic fire or other disturbance. Developing on acidic, nutrient-poor, and very well-drained soils within a few kilometers of the ocean, they may occur as heathlands, grasslands, or support a patchwork of grass and shrub vegetation. Characteristic species include Amelanchier nantucketensis, Arctostaphylos uva-ursi, Carex pensylvanica, Corema conradii, Deschampsia flexuosa, Gaylussacia baccata, Hudsonia ericoides, Hudsonia tomentosa, Schizachyrium scoparium, and Vaccinium angustifolium. Human disturbances may be partly responsible for the origins of these grasslands and heathlands (Motzkin and Foster 2002).

On rocky headlands of northern New England and Canadian Maritime Provinces, Juniperus horizontalis and Juniperus communis may occur, with Empetrum nigrum, Plantago maritima, Solidago sempervirens, and Ligusticum scoticum. Dwarf heath-grassland is dominated by Festuca rubra, Aronia melanocarpa (= Photinia melanocarpa), Symphyotrichum novi-belgii, Vaccinium angustifolium, Vaccinium vitis-idaea, among others. Low coastal shrublands are Gaylussacia baccata- or Gaylussacia dumosa-dominated. Tall shrublands are dominated by Alnus incana ssp. rugosa, Ilex mucronata (= Nemopanthus mucronatus), Aronia x prunifolia (= Photinia floribunda), Prunus pensylvanica, and Viburnum nudum. Gaylussacia baccata and Morella pensylvanica occur in the understory. Common herbs include Pteridium aquilinum var. latiusculum, Trientalis borealis, and Maianthemum canadense (S. Basquill pers. comm. 2015).

Along the South Atlantic Coast, Panicum amarum and Uniola paniculata are characteristic on the foredunes, and Spartina patens (= var. monogyna) and Schizachyrium littorale on the older dunes and sand flats. Iva imbricata is a characteristic shrub. Examples along the Gulf Coast contain Ceratiola ericoides, Chrysoma pauciflosculosa, Helianthemum arenicola, Paronychia erecta, and Schizachyrium maritimum. On the western Gulf Coast, this macrogroup includes ridges dominated by Schizachyrium littorale and a mixture of forbs, and swales dominated by Andropogon gerardii, Muhlenbergia capillaris, Paspalum monostachyum, and Sorghastrum nutans.

Dunes in the northern Great Lakes region, especially Lake Superior, shift in composition. A description is needed.

Dynamics:  The environment of this macrogroup is one of the most dynamic in existence for terrestrial vegetation. The dunes are reworked by storms or by more gradual eolian processes that may completely change the local environment in a short time. Many of these sites are fairly early in the process of primary succession on recent surfaces. The sandy sites found in this macrogroup are influenced by wind deposition, including active dune processes of wind-caused "blowouts" and subsequent restabilization. Environmental processes include sand deposition, sand erosion, and stabilization. Along the Atlantic and Gulf coasts, overwash, erosion, and sea spray from storms occur often. Hurricanes and lesser storms significantly alter this vegetation on a regular basis. Vegetation interacts strongly with geologic processes with the presence of grass an important factor in the development of new dunes. Alteration of dynamic processes, such as artificial enhancement of dunes by planting or sand fencing, can have drastic effects on this vegetation, causing large areas to succeed to woody vegetation.

Great Lakes dunes are relatively young, as the Great Lakes were occupied by ice until approximately 16,000 years ago. The dune sands are derived from glacial sediments, including lacustrine and outwash sands and sandy tills. Most of the larger dune complexes are associated with the Lake Nipissing stage of the Great Lakes, when water levels were 7.6 to 9 m (25-30 feet) higher than present-day lake levels (Dorr and Eschman 1970, cited in Kost et al. 2007). These higher lake levels resulted in greater amounts of coastal erosion and dune formation. A combination of water erosion and wind deposition resulted in the formation of Great Lakes coastal dunes. The sand source for the coastal dunes was glacial sediment that was eroded by streams and by waves eroding bluffs along the Great Lakes shoreline. These sediments were then moved along the Great Lakes shoreline by near-shore currents, and then deposited along the shoreline by wave action. Strong winds then carried the sands inland, creating dunes. Blowouts, sand burial and abrasion, excessively well-drained and droughty soils, desiccating winds, and occasional fires maintain open conditions (Kost et al. 2007). Great Lakes dunes have been negatively impacted by residential development.

On dunes in the Northeast, this vegetation has been altered by hardening of shorelines, trampling, off-road vehicle traffic, and residential development. Barrier islands may be heavily grazed by wild horses.

Environmental Description:  This macrogroup occurs on well-drained to excessively well-drained sands near shorelines along the Great Lakes, and Atlantic and Gulf coasts. Sites in the Great Lakes include beaches, embayments, sandplains and dunes, and include the full range of dune types, including foredunes, parallel dunes, parabolic dunes, perched dunes, blowouts, and barrier dunes (Kost et al. 2007). Along the Atlantic and Gulf coasts, sites also occur on coastal strands and barrier islands. Rocky headlands support this vegetation on the North Atlantic Coast. Soils are low in nutrient-holding capacity and have little or no horizon development. Sand movement across dunes, including dunal blowouts, strongly impact this macrogroup. Along the Atlantic and Gulf coasts, salt spray provides a source of nutrients and can strongly impact vegetation patterns.

Geographic Range: This macrogroup occurs along the Great Lakes shores of the United States and Canada ranging from Wisconsin to Ontario and New York and along the Atlantic Coast from the Maritime Provinces to southern Florida and along the Gulf Coast to Texas.

Nations: CA,MX,US

States/Provinces:  AL, CT, DE, FL, GA, IL, IN, LA, MA, MD, ME, MI, MN, MS, NB, NC, NH, NJ, NS, NY, OH, ON, PA, PE, QC?, RI, SC, TX, VA, VT, WI




Confidence Level: Moderate

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: > Myrica thicket (Chrysler 1930)
>< Beach Dune (FNAI 1990)
>< Coastal Grassland (FNAI 1990)
> Coastal Heathland and Sandplain Grassland (Dunwiddie et al. 1996)
> Middle beach (Chrysler 1930)
> Upper beach (Chrysler 1930)

Concept Author(s): M.A. Chrysler (1930); H.J. Oosting and W.D. Billings (1942); D.A. Albert (1995b); S.C. Gawler and A. Cutko (2010)

Author of Description: S. Menard, L. Sneddon, J. Cohen, and D. Faber-Langendoen

Acknowledgements: We have incorporated significant descriptive information previously compiled by Jim Drake, Sue Gawler and Sean Basquill.

Version Date: 05-21-15

  • Albert, D. A. 1995b. Regional landscape ecosystems of Michigan, Minnesota, and Wisconsin: A working map and classification. General Technical Report NC-178. USDA Forest Service, North Central Forest Experiment Station, St. Paul, MN. 250 pp. plus maps.
  • Albert, D. A. 2006. Borne of the wind: An introduction to the ecology of Michigan sand dunes. University of Michigan Press, Ann Arbor, MI. 63 pp.
  • Bach, D. P. 1978. Plant communities, habitats, and soil conditions of Grand Sable Dunes, Pictured Rocks National Lakeshore, Michigan. Masters thesis, Michigan Technical University, Houghton, MI. 180 pp.
  • Chrysler, M. A. 1930. The origin and development of the vegetation of Sandy Hook. Bulletin of the Torrey Botanical Club 57:163-176.
  • Cohen, J. G., M. A. Kost, B. S. Slaughter, and D. A. Albert. 2015. A field guide to the natural communities of Michigan. Michigan State University Press, East Lansing, MI. 362 pp.
  • Cowles, H. C. 1899. The ecological relations of the vegetation on the sand dunes of Lake Michigan. Botanical Gazette 27:95-117, 167-202, 281-308, 361-396.
  • Curtis, J. T. 1959. The vegetation of Wisconsin: An ordination of plant communities. Reprinted in 1987. University of Wisconsin Press, Madison. 657 pp.
  • Dunwiddie, P. W., R. E. Zaremba, and K. A. Harper. 1996. A classification of coastal heathlands and sandplain grasslands in Massachusetts. Rhodora 98(894):117-145.
  • FNAI [Florida Natural Areas Inventory]. 1990. Guide to the natural communities of Florida. Florida Natural Areas Inventory and Florida Department of Natural Resources, Tallahassee. 111 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]
  • Gawler, S. C., and A. Cutko. 2010. Natural landscapes of Maine: A classification of vegetated natural communities and ecosystems. Maine Natural Areas Program, Department of Conservation, Augusta.
  • 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]
  • Lichter, J. 1998. Primary succession and forest development on coastal Lake Michigan sand dunes. Ecological Monographs 68(4):487-510.
  • Martin, W. E. 1959b. The vegetation of Island Beach State Park, New Jersey. Ecological Monographs 29:1-46.
  • Motzkin, G., and D. R. Foster. 2002. Grasslands, heathlands and shrublands in coastal New England: Historical interpretations and approaches to conservation. Journal of Biogeography 29:1569-1590. [http://harvardforest.fas.harvard.edu/sites/harvardforest.fas.harvard.edu/files/publications/pdfs/Motzkin_JBiogeography_2002_Grasslands.pdf]
  • Oosting, H. J., and W. D. Billings. 1942. Factors affecting vegetational zonation on coastal dunes. Ecology 23:131-142.
  • Stalter, R. 1974. Vegetation in coastal dunes of South Carolina. Castanea 39:95-103.
  • van der Valk, A. G. 1975b. The floristic composition and structure of foredune plant communities of Cape Hatteras National Seashore. Chesapeake Science 16:115-126.