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CEGL004467 Clethra alnifolia - Toxicodendron vernix / Aristida stricta - Osmunda cinnamomea - Sarracenia spp. Shrub Seepage Meadow
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Coastal Sweet-pepperbush - Poison-sumac / Pineland Three-awn - Cinnamon Fern - Pitcherplant species Shrub Seepage Meadow
Colloquial Name: Mucky Sandhill Hillside Seep
Hierarchy Level: Association
Type Concept: This type covers seepage-fed herbaceous or shrub-herb wetlands of sandhills terrain found primarily in the Sandhills region but present in scarps and sand ridges elsewhere in the Coastal Plain of North Carolina and South Carolina. These are generally small areas on slopes, but can occur at slope bases where water is forced to the surface by a clay layer and soil conditions are permanently saturated. These communities are rare in the North Carolina Sandhills and on Fort Bragg and Camp MacKall, where they are usually found in high-moisture, open-canopied transitional areas located between streams (or impoundments) and seepage-fed slopes. The permanently saturated conditions of these sites most likely help to retard shrub and tree encroachment. Dominant species include Sarracenia flava, Sphagnum spp., Carex exilis, Rhynchospora stenophylla, Danthonia epilis, Xyris fimbriata, Xyris chapmanii, Eupatorium resinosum, and Rhexia spp. Sandhill seeps consist of a dense to open growth of various wetland shrubs and herbs, or mixtures of wetland and upland species, with structure determined by fire regime. Common shrubs include Clethra alnifolia, Lyonia lucida, Aronia arbutifolia, Ilex glabra, Gaylussacia frondosa, Symplocos tinctoria, Morella caroliniensis, and Toxicodendron vernix. A variety of other shrubs may be present in some sites. Arundinaria tecta may dominate in places, especially in frequently burned sites. Osmunda cinnamomea often dominates annually burned sites. Canopy species include Pinus serotina, Pinus palustris, and Liquidambar styraciflua. Acer rubrum, Magnolia virginiana, and Persea palustris are often present in the midstory. Herbs are sparse under shrub cover but may dominate frequently burned sites. Typical herbs include Osmunda cinnamomea, Xyris caroliniana, Pteridium aquilinum, Woodwardia virginica, Dichanthelium spp., Andropogon glomeratus, Ctenium aromaticum, Sarracenia flava, Sarracenia purpurea, Sarracenia rubra, Drosera capillaris, Rhexia alifanus, Polygala lutea, Eupatorium pilosum, and Aristida stricta. Sphagnum spp. are common. On frequently burned sites a great diversity of other herbs may also be present. Community structure is strongly controlled by fire regime. Because of their small size, Sandhill Seeps are subject to fires spreading from adjacent sandhill communities, and under natural fire regimes they probably burned more frequently than other similarly wet communities. At least parts of them burned almost as frequently as the adjoining sandhill communities. Under frequent fire Sandhill seeps are open and herb-dominated. In the absence of fire shrubs quickly expand and the vegetation becomes pocosin-like. The nutrient dynamics of these communities are not known. The presence of clay in the soil may allow greater retention of nutrients than in sandy soils, although the seepage is likely to be very low in nutrients. Like other small communities in sandhill areas, nutrients mobilized by fire may be available to Sandhill seeps even if they do not themselves burn. These communities are distinguished by the occurrence of wetland vegetation on seepage slopes. The boundary with Streamhead Pocosin may be difficult to determine in some areas. In infrequently burned areas where both are shrubby, Sandhill seeps may be recognized by partial or total isolation from a stream system, location on a sharp slope break, or by remnants of the herbaceous vegetation beneath the shrubs. Herb-dominated Sandhill seeps may be distinguished by their occurrence on relatively small, sloping, seepage-fed areas in sandhills.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: In very frequently burned (every 1-2 years) seepage areas on Fort Bragg, these communities had extremely high species richness, with up to 102 species per 1/100 hectare (10x10 m) (NC Vegetation Survey 1989), the highest known species richness in temperate North America. Those seeps may represent unusually rich examples, but many Sandhill Seeps had fairly diverse herbaceous vegetation that has gradually disappeared with the lack of fire. It is unclear how common Sandhill Seeps are. They may be fairly widespread in the northern part of the Sandhills region, in Moore and Hoke counties, North Carolina, but they have always been of limited acreage. Because they so quickly become overgrown with shrubs, examples in good condition are now extremely rare, except for on Fort Bragg, where marginal to good examples are common. Numerous examples of high-quality seeps are most likely present in the annually burned impact areas.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: Dominant species include Sarracenia flava, Sphagnum spp., Carex exilis, Rhynchospora stenophylla, Danthonia epilis, Xyris fimbriata, Xyris chapmanii, Eupatorium resinosum, and Rhexia spp. Sandhill seeps consist of a dense to open growth of various wetland shrubs and herbs, or mixtures of wetland and upland species, with structure determined by fire regime. Common shrubs include Clethra alnifolia, Lyonia lucida, Aronia arbutifolia, Ilex glabra, Gaylussacia frondosa, Symplocos tinctoria, Morella caroliniensis (= Myrica heterophylla), and Toxicodendron vernix. A variety of other shrubs may be present in some sites. Arundinaria tecta (= Arundinaria gigantea ssp. tecta) may dominate in places, especially in frequently burned sites. Osmunda cinnamomea often dominates annually burned sites. Canopy species include Pinus serotina, Pinus palustris, and Liquidambar styraciflua. Acer rubrum, Magnolia virginiana, and Persea palustris are often present in the midstory. Herbs are sparse under shrub cover but may dominate frequently burned sites. Typical herbs include Osmunda cinnamomea, Xyris caroliniana, Pteridium aquilinum, Woodwardia virginica, Dichanthelium spp., Andropogon glomeratus, Ctenium aromaticum, Sarracenia flava, Sarracenia purpurea, Sarracenia rubra, Drosera capillaris, Rhexia alifanus, Polygala lutea, Eupatorium pilosum, and Aristida stricta. Sphagnum spp. are common. On frequently burned sites a great diversity of other herbs may also be present. Sandhills bog lily, which is a rare endemic of the Sandhills, is a newly described species named Lilium pyrophilum (Skinner and Sorrie 2002).
Dynamics: Community structure is strongly controlled by fire regime. Because of their small size, Sandhill Seeps are subject to fires spreading from adjacent sandhill communities, and under natural fire regimes they probably burned more frequently than other similarly wet communities. At least parts of them burned almost as frequently as the adjoining sandhill communities. Under frequent fire Sandhill seeps are open and herb-dominated. In the absence of fire shrubs quickly expand and the vegetation becomes pocosin-like. The nutrient dynamics of these communities are not known. The presence of clay in the soil may allow greater retention of nutrients than in sandy soils, although the seepage is likely to be very low in nutrients. Like other small communities in sandhill areas, nutrients mobilized by fire may be available to Sandhill seeps even if they do not themselves burn.
Environmental Description: These communities are found on slopes in sand ridge or sandhill areas where water is forced to the surface by a clay layer. Soils are wet sands underlain by clays, usually mapped as Blaney (Arenic Hapludults) or Vaucluse (Typic Hapludults) loamy sands but probably representing inclusions in these map units. Soil series may include Fuquay (Plinthic Paleudults) and Lakeland (Typic Quartzipsamments) sands; Gilead (Aquic Hapludults), Pactolus (Aquic Quartzipsamments) and Stallings (Aeric Paleaquults) loamy sands; Torhunta coarse-loamy soils (Typic Humaquepts); and Johnston loam (Cumulic Humaquepts). Sites that support this community are permanently saturated with oligotrophic waters.
Geographic Range: This type covers seepage-fed herbaceous or shrub-herb wetlands of sandhills terrain found primarily in the Sandhills region but present in scarps and sand ridges elsewhere in the Coastal Plain of North Carolina and South Carolina.
Nations: US
States/Provinces: NC, SC
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.683923
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.C Shrub & Herb Wetland Subclass | S44 | 2.C |
Formation | 2.C.4 Temperate to Polar Freshwater Marsh, Wet Meadow & Shrubland Formation | F013 | 2.C.4 |
Division | 2.C.4.Ne Atlantic & Gulf Coastal Marsh, Wet Meadow & Shrubland Division | D322 | 2.C.4.Ne |
Macrogroup | 2.C.4.Ne.2 Beaksedge species - Spikerush species - Panicgrass species Atlantic & Gulf Coastal Plain Wet Prairie & Marsh Macrogroup | M067 | 2.C.4.Ne.2 |
Group | 2.C.4.Ne.2.e Beaksedge species - Pitcherplant species Seep Group | G187 | 2.C.4.Ne.2.e |
Alliance | A1463 Feather-bristle Beaksedge - Pitcherplant species - Toothache Grass Seep Alliance | A1463 | 2.C.4.Ne.2.e |
Association | CEGL004467 Coastal Sweet-pepperbush - Poison-sumac / Pineland Three-awn - Cinnamon Fern - Pitcherplant species Shrub Seepage Meadow | CEGL004467 | 2.C.4.Ne.2.e |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: ? Sandhill Seep (Bog Variant) (TNC and NCNHP 1993)
- 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.
- North Carolina Vegetation Survey. No date. Unpublished data.
- 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.
- Schafale, Mike P. Personal communication. Ecologist, North Carolina Department of Environment, Health, and Natural Resources, Division of Parks and Recreation, Natural Heritage Program, Raleigh.
- Skinner, M. W., and B. A. Sorrie. 2002. Conservation and ecology of Lilium pyrophilum, a new species of Liliaceae from the Sandhills region of the Carolinas and Virginia, U.S.A. Novon 12:94-105.
- Southeastern Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Durham, NC.
- TNC and NCNHP [The Nature Conservancy and North Carolina Natural Heritage Program]. 1993. Rare and endangered plant survey and natural area inventory for Fort Bragg and Camp MacKall military reservations, North Carolina. Unpublished report by M. J. Russo, B. A. Sorrie, B. van Eerden, and T. Hippensteel, The Nature Conservancy and North Carolina Division of Parks and Recreation, Department of Environment, Health, and Natural Resources, Raleigh, NC.