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CEGL003818 Rhododendron catawbiense Shrubland
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Catawba Rosebay Shrubland
Colloquial Name: Southern Appalachian Catawba Rosebay Heath Bald
Hierarchy Level: Association
Type Concept: This evergreen shrubland occurs at the highest elevations, typically 1500-1980 m (5000-6500 feet), in the southern Appalachian Mountains on steep, exposed slopes, ridges, and rock outcrops. It occurs primarily in the northern portion of the Southern Appalachians, north of the Asheville Basin, in mountain ranges lacking Pieris floribunda and Rhododendron carolinianum. Greater than 75% of the shrub cover is composed of evergreen species, and the predominant shrub is Rhododendron catawbiense. Scattered trees contribute less than 1% cover, typically Aronia melanocarpa, Abies fraseri, and Picea rubens. Small openings in the shrub canopy are dominated by rock or herbs. Herb cover beneath the shrub canopy is absent or very sparse (<5%) and may include Gaultheria procumbens, Galax urceolata, Epigaea repens, Medeola virginiana, Trillium undulatum, Melampyrum lineare, Dryopteris campyloptera, Houstonia serpyllifolia, Viola spp., and Carex debilis var. rudgei. Mosses may be locally dominant at the base of Rhododendron clumps, often Polytrichum commune or bryophytes from adjacent Picea - Abies communities. This community can result from secondary succession after fire or logging or can occur as a topo-edaphic climax on steep, exposed sites. Occurrences may range in size from 0.5-200 hectares. This community can grade into or occur adjacent to high-elevation rock outcrop communities, montane grass-dominated communities, or forests dominated by Picea rubens, Abies fraseri, and northern hardwood species such as Fagus grandifolia, Acer saccharum, and Betula alleghaniensis.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This community can grade into or occur adjacent to high-elevation rock outcrop communities, montane grass-dominated communities, or forests dominated by Picea rubens, Abies fraseri, and northern hardwood species such as Fagus grandifolia, Acer saccharum, and Betula alleghaniensis. A more open, low-growing, evergreen shrubland, ~Leiophyllum buxifolium Dwarf-shrubland (CEGL003951)$$, is restricted to areas where Leiophyllum buxifolium dominates areas greater than 0.1 hectare. However, the species may be locally dominant as inclusions in this shrubland. Similar, but floristically different, ericaceous shrublands occur in the Mahoosuc Mountains of Maine (Fahey 1976). Exemplary occurrences are known from the Roan Mountain Massif, North Carolina and Tennessee, and Mount Rogers, Virginia.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: Greater than 75% of the shrub cover is composed of evergreen species, and the predominant shrub is Rhododendron catawbiense, which forms a continuous, dense shrub canopy from 1-4 m tall. On the most rugged, windswept sites, shrubs are stunted and gnarled. The occurrence and relative abundance of associated shrub species vary with elevation and adjacent vegetation. Scattered trees contribute less than 1% cover, typically Aronia melanocarpa, Abies fraseri, and Picea rubens. Small openings in the shrub canopy are dominated by rock or herbs. Herb cover beneath the shrub canopy is absent or very sparse (<5%) and may include Gaultheria procumbens, Galax urceolata, Epigaea repens, Medeola virginiana, Trillium undulatum, Melampyrum lineare, Dryopteris campyloptera, Houstonia serpyllifolia, Viola spp., and Carex debilis var. rudgei. Mosses may be locally dominant at the base of Rhododendron clumps, often Polytrichum commune or bryophytes from adjacent Picea - Abies communities. This community contains species endemic to the southern Appalachian Mountains, including Abies fraseri, Fothergilla major, Galax urceolata, Geum radiatum, Houstonia purpurea var. montana, Houstonia serpyllifolia, Hudsonia montana, Hypericum buckleii, Liatris helleri, Lilium grayi, Menziesia pilosa, Pieris floribunda, Prenanthes roanensis, Rhododendron vaseyi, Rhododendron carolinianum, Aronia melanocarpa, and Vaccinium erythrocarpum. Species occurring disjunct from their typical northern distributions include Alnus viridis ssp. crispa, Dryopteris campyloptera, Picea rubens, and Vaccinium corymbosum.
Dynamics: Windfall, landslides, and small, localized and lightning-caused fires are important in the establishment and maintenance of this community. This community can result from secondary succession after fire or logging, in which case it is unstable and will eventually succeed to a forest community with a Rhododendron understory (e.g., ~Picea rubens - (Abies fraseri) / (Rhododendron catawbiense, Rhododendron maximum) Forest (CEGL007130)$$). When this community occurs on steep, exposed sites, where wind exposure, soil infertility, and drought maintain a scrubby shrub community, it is a topo-edaphic climax. According to Gant (1978) Rhododendron catawbiense heath balds represent stable communities that employ allelopathic interference to arrest succession and maintain themselves.
Environmental Description: This evergreen shrubland occurs at the highest elevations, typically 1500-1980 m (5000-6500 feet), in the southern Appalachian Mountains on steep, exposed slopes, ridges, and rock outcrops. It occurs primarily in the northern portion of the Southern Appalachians, north of the Asheville Basin, in mountain ranges lacking Pieris floribunda and Rhododendron carolinianum. This community can result from secondary succession after fire or logging or can occur as a topo-edaphic climax on steep, exposed sites. Occurrences may range in size from 0.5-200 hectares. This community can grade into or occur adjacent to high-elevation rock outcrop communities, montane grass-dominated communities, or forests dominated by Picea rubens, Abies fraseri, and northern hardwood species such as Fagus grandifolia, Acer saccharum, and Betula alleghaniensis.
Geographic Range: This community occurs primarily in the northern portion of the Southern Appalachians, north of the Asheville Basin, in North Carolina, Tennessee, and Virginia.
Nations: US
States/Provinces: GA?, NC, TN, VA
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.687414
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G2
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 2 Shrub & Herb Vegetation Class | C02 | 2 |
Subclass | 2.B Temperate & Boreal Grassland & Shrubland Subclass | S18 | 2.B |
Formation | 2.B.2 Temperate Grassland & Shrubland Formation | F012 | 2.B.2 |
Division | 2.B.2.Nc Eastern North American Grassland & Shrubland Division | D024 | 2.B.2.Nc |
Macrogroup | 2.B.2.Nc.1 Catawba Rosebay / Michaux''s Saxifrage - Flattened Oatgrass Felsic & Mafic Scrub & Grassland Macrogroup | M506 | 2.B.2.Nc.1 |
Group | 2.B.2.Nc.1.a Catawba Rosebay - Mountain Fetterbush - Mountain Alder Southern Appalachian Shrub Bald Group | G658 | 2.B.2.Nc.1.a |
Alliance | A0744 Catawba Rosebay - Carolina Azalea - Mountain Laurel Shrub Bald Alliance | A0744 | 2.B.2.Nc.1.a |
Association | CEGL003818 Catawba Rosebay Shrubland | CEGL003818 | 2.B.2.Nc.1.a |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: > Rhododendron catawbiense - Menziesia pilosa Subtype (Fleming and Coulling 2001)
> Sorbus americana / Menziesia pilosa - Vaccinium erythrocarpum - Rubus canadensis Subtype (Fleming and Coulling 2001)
< IC4a. Heath Bald Shrubland (Allard 1990)
> Sorbus americana / Menziesia pilosa - Vaccinium erythrocarpum - Rubus canadensis Subtype (Fleming and Coulling 2001)
< IC4a. Heath Bald Shrubland (Allard 1990)
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- Brown, D. M. 1941. Vegetation of Roan Mountain: A phytosociological and successional study. Ecological Monographs 11:61-97.
- Chafin, L. 2011. Georgia''s natural communities and associated rare plant and animal species: Thumbnail accounts. Based on "Guide to the Natural Communities of Georgia," by Edwards et al. 2013. University of Georgia Press. Georgia Nongame Conservation Section, Wildlife Resources Division, Georgia Department of Natural Resources. 125 pp.
- Fahey, T. J. 1976. The vegetation of a heath bald in Maine. Bulletin of the Torrey Botanical Club 103:23-29.
- Fleming, G. P., K. D. Patterson, and K. Taverna. 2017. The natural communities of Virginia: A classification of ecological community groups and community types. Third approximation. Version 3.0. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond, VA. [http://www.dcr.virginia.gov/natural-heritage/natural-communities/]
- Fleming, G. P., and K. D. Patterson. 2009a. A vegetation classification for the Appalachian Trail: Virginia south to Georgia. Virginia Department of Conservation and Recreation, Division of Natural Heritage. In-house analysis, March 2009.
- Fleming, G. P., and P. P. Coulling. 2001. Ecological communities of the George Washington and Jefferson national forests, Virginia. Preliminary classification and description of vegetation types. Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond, VA. 317 pp.
- Gant, R. E. 1978. The role of allelopathic interference in the maintenance of Southern Appalachian heath balds. Ph.D. dissertation, University of Tennessee, Knoxville. 123 pp.
- Ramseur, G. S. 1958. The vascular flora of high mountain communities of the Southern Appalachians. Ph.D. dissertation, University of North Carolina, Chapel Hill. 106 pp.
- Rawinski, T. J. 1992. A classification of Virginia''s indigenous biotic communities: Vegetated terrestrial, palustrine, and estuarine community classes. Unpublished document. Virginia Department of Conservation and Recreation, Division of Natural Heritage. Natural Heritage Technical Report No. 92-21. Richmond, VA. 25 pp.
- Risk, P. L. 1993. High elevation heath communities in the Blue Ridge of North Carolina. Ph.D. dissertation, University of North Carolina, Chapel Hill.
- Schafale, M. P. 2012. Classification of the natural communities of North Carolina, 4th Approximation. North Carolina Department of Environment, Health, and Natural Resources, Division of Parks and Recreation, Natural Heritage Program, Raleigh.
- 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.
- Southeastern Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Durham, NC.
- Weakley, A. S., compiler. 1993. Natural Heritage Program list of the rare plant species of North Carolina. North Carolina Department of Environment, Health, and Natural Resources, Division of Parks and Recreation, Natural Heritage Program. Raleigh. 79 pp.
- Whittaker, R. H. 1979a. Appalachian balds and other North American heathlands. Pages 427-439 in: R. L. Specht, editor. Ecosystems of the world. Series Publication 9A. Heathlands and related shrublands: Descriptive studies. Elsevier Scientific Publishing Company, New York.