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CEGL003768 Pinus rigida - Quercus alba / Sporobolus heterolepis - Andropogon gerardii Woodland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Pitch Pine - White Oak / Prairie Dropseed - Big Bluestem Woodland

Colloquial Name: Southern Blue Ridge Ultramafic Outcrop Barrens (Pitch Pine Woodland Type)

Hierarchy Level:  Association

Type Concept: This community occurs on shallow, rocky soils associated with outcrops of serpentinized olivine in the Southern Blue Ridge. It is a unique community with a restricted range and few known occurrences. This community includes open woodland vegetation dominated by stunted Pinus rigida and Quercus alba, occurring over a cespitose graminoid-dominated understory with little shrub cover. Although the relative basal area for the two canopy species is the same, Pinus rigida is twice as dense as Quercus alba. Other canopy and subcanopy trees may include Tsuga canadensis, Acer rubrum, and Oxydendrum arboreum. The dense herbaceous stratum is dominated by Andropogon gerardii, Sporobolus heterolepis, and Schizachyrium scoparium. Common forbs include Packera plattensis, Hexastylis arifolia var. ruthii, and Thalictrum macrostylum.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: Seepage areas dominated by Osmunda regalis var. spectabilis and Parnassia grandifolia, with Sanguisorba canadensis, Oxypolis rigidior, and Panicum virgatum, occur as inclusions in this woodland. This community is endemic to Buck Creek, Clay County, North Carolina.

Similar vegetation occurs in association with serpentine soils in the southwestern Piedmont of Virginia (Rawinski 1992) and is distinguished by the dominance of Pinus virginiana and other significant differences in floristic composition. Physiognomically similar vegetation occurs on serpentine in the northwestern United States as well as in Maryland and Pennsylvania.

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

Physiognomy and Structure: No Data Available

Floristics: These open woodlands have canopies dominated by stunted Pinus rigida and Quercus alba. Although the relative basal area for the two species is the same, Pinus rigida is twice as dense as Quercus alba. Other canopy and subcanopy trees may include Tsuga canadensis, Acer rubrum, and Oxydendrum arboreum. Shrub cover is sparse, typically forming less than 10% coverage and occurring in clumps. Shrub species include Physocarpus opulifolius, Viburnum nudum var. cassinoides, Vaccinium stamineum, Kalmia latifolia, and a low, stoloniferous form of Rhododendron viscosum. Smilax glauca is a common vine. The dense herbaceous stratum is dominated by cespitose graminoids, most commonly Andropogon gerardii, Sporobolus heterolepis, and Schizachyrium scoparium. Common forbs include Packera plattensis (= Senecio plattensis), Hexastylis arifolia var. ruthii, and Thalictrum macrostylum. Other herbaceous species known to occur in this community include Poa saltuensis, Muhlenbergia glomerata, Danthonia spicata, Danthonia compressa, Sorghastrum nutans, Panicum virgatum, Dichanthelium dichotomum, Dichanthelium boscii, Elymus trachycaulus ssp. trachycaulus, Deschampsia cespitosa, Castilleja coccinea, Carex woodii, Symphyotrichum undulatum (= Aster undulatus), Symphyotrichum laeve (= Aster laevis), Oenothera fruticosa, Thaspium trifoliatum, and Phlox stolonifera. Regionally uncommon species or species disjunct from their main distributions include Carex woodii, Deschampsia cespitosa (= ssp. glauca), Elymus trachycaulus, Frasera caroliniensis, Gentianopsis crinita, Muhlenbergia glomerata, Pedicularis lanceolata, Poa saltuensis, Polygala paucifolia, Polygala senega, Packera plattensis, and Sporobolus heterolepis (Schafale and Weakley 1990).

Dynamics:  The open, grassy woodland structure of this community is probably determined by a combination of site conditions and periodic disturbances. The dry grassy vegetation is flammable and recovery of woody species following a fire may be slow. The natural fire frequency for this woodland is not known. In the absence of occasional fire, shrub density increases and herbaceous cover decreases. However, the overstory composition and structure is likely maintained, at least in part, by the harsh soil conditions. Within the past 30 years, the overstory in this community has been significantly reduced because of infestations of southern pine beetle. Periodic fire will help maintain the graminoid-dominated understory. Fire should be applied with the objective of maintaining a physiognomic complex of woodland, forest, and grass-dominated areas.

Environmental Description:  This community occurs on shallow, rocky soils associated with outcrops of serpentinized olivine in the Southern Blue Ridge. These circumneutral soils are high in magnesium and have low water-holding capacity (Mansberg and Wentworth 1984). This woodland is found at moderate elevations (1015 m) on gentle to steep slopes with a western or southwestern exposure.

Geographic Range: This community is endemic to Buck Creek, Clay County, North Carolina, in the Southern Blue Ridge.

Nations: US

States/Provinces:  NC




Confidence Level: Moderate

Confidence Level Comments: No Data Available

Grank: G1

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: < IE9b. Blue Ridge/Piedmont Ultramafic Barren (Allard 1990)
? Pitch Pine - Oak (15) (USFS 1988)

Concept Author(s): K.D. Patterson and G. Kauffman

Author of Description: K.D. Patterson

Acknowledgements: No Data Available

Version Date: 02-23-95

  • Allard, D. J. 1990. Southeastern United States ecological community classification. Interim report, Version 1.2. The Nature Conservancy, Southeast Regional Office, Chapel Hill, NC. 96 pp.
  • Fleming, Gary P. Personal communication. Ecologist, Virginia Department of Conservation and Recreation, Division of Natural Heritage, Richmond, VA.
  • Kauffman, Gary. Personal communication. Botanist. USDA Forest Service, Nantahala National Forest, Highlands, NC.
  • Mansberg, L., and T. R. Wentworth. 1984. Vegetation and soils of a serpentine barren in western North Carolina. Bulletin of the Torrey Botanical Club 111:273-286.
  • Peet, R. K., T. R. Wentworth, M. P. Schafale, and A.S. Weakley. No date. Unpublished data of the North Carolina Vegetation Survey. University of North Carolina, Chapel Hill.
  • 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.
  • 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.
  • USFS [U.S. Forest Service]. 1988. Silvicultural examination and prescription field book. USDA Forest Service, Southern Region. Atlanta, GA. 35 pp.
  • Weakley, A. S. 2010. Flora of the Carolinas, Virginia, Georgia, and surrounding areas. Unpublished working draft. University of North Carolina Herbarium (NCU), North Carolina Botanical Garden, University of North Carolina, Chapel Hill. [http://www.herbarium.unc.edu/flora.htm]