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CEGL007044 Gordonia lasianthus - Magnolia virginiana - Persea palustris / Sphagnum spp. Swamp Forest
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Loblolly-bay - Sweetbay - Swamp Bay / Peatmoss species Swamp Forest
Colloquial Name: Loblolly-bay Swamp Forest
Hierarchy Level: Association
Type Concept: These forests occur in saturated, peat-filled seepage depressions usually located at the base of sandy slopes but also at the edges of floodplains or other flat areas with high water tables. The southern limit of this community is just north of Lake Okeechobee, Florida; the community extends northward through Georgia and South Carolina to North Carolina, where Gordonia lasianthus reaches the limit of its distribution. The closed, broad-leaved evergreen canopy is composed of Magnolia virginiana, Persea palustris, and Gordonia lasianthus. A patchy understory of shrubs Cyrilla racemiflora, Clethra alnifolia, Itea virginica, Lyonia lucida, and Ilex glabra and vines Smilax laurifolia, Smilax glauca, and Vitis rotundifolia occurs with an abundant to sparse layer of ferns Woodwardia areolata and Osmunda cinnamomea. Sphagnum mats are interlaced with exposed tree roots. In northeastern Florida, at the Timucuan Ecological and Historic Preserve, dead and dying Persea palustris indicate that these loblolly-bay forests are being affected by laurel wilt, which is caused by a vascular wilt fungus that is transmitted to species in the Lauraceae family via. the non-native redbay ambrosia beetle (Xyleborus glabratus).
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This association description was written for a generalized concept of a bay forest and may need reassessment and refinement.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: The closed, broad-leaved evergreen canopy is composed of Magnolia virginiana, Persea palustris, and Gordonia lasianthus. A patchy understory of shrubs Cyrilla racemiflora, Clethra alnifolia, Itea virginica, Lyonia lucida, and Ilex glabra and vines Smilax laurifolia, Smilax glauca, and Vitis rotundifolia occurs with an abundant to sparse layer of ferns Woodwardia areolata and Osmunda cinnamomea. Sphagnum mats are interlaced with exposed tree roots. Additional species found on Ocala National Forest include Quercus nigra, Pinus serotina, Vaccinium fuscatum, Gelsemium sempervirens, Morella cerifera, Nyssa biflora, Serenoa repens, Ilex cassine, Smilax smallii, and Viburnum nudum. Exotics include Triadica sebifera (= Sapium sebiferum) and Ligustrum sinense.
Dynamics: Baygalls are seldom dry enough to burn, thus the fire interval is probably 50 to 100 years or more (FNAI 1990). However, Clewell (1971) estimated the fire-return interval to be less than 45 years. When fires are not too severe, many species are usually able to resprout (FNAI 1990). These forests are probably prone to some infrequent, but perhaps moderate-intensity wildfire. Once Gordonia lasianthus is tree-sized, its thick bark provides some protection from fire. Hurricanes could cause blowdown.
This community succeeds from Atlantic white-cedar swamp forest and pond pine woodland in the absence of fire, and may revert to these types following fire if the subsurface peat is not burned. Areas where peat is consumed by fire may serve as Pinus elliottii regeneration sites. If only a small amount of surface peat is removed, this community may be replaced by a wet flatwoods. If much of the surface layer is decreased, Baygalls will be invaded by willows and then change to a cypress-gum community. With recurrent fires, a shrub bog results (Clewell 1971, FNAI 1990).
In northeastern Florida, at the Timucuan Ecological and Historic Preserve, dead and dying Persea palustris indicate that these loblolly-bay forests are being affected by laurel wilt, which is caused by a vascular wilt fungus that is transmitted to species in the Lauraceae family via. the non-native redbay ambrosia beetle (Xyleborus glabratus).
This community succeeds from Atlantic white-cedar swamp forest and pond pine woodland in the absence of fire, and may revert to these types following fire if the subsurface peat is not burned. Areas where peat is consumed by fire may serve as Pinus elliottii regeneration sites. If only a small amount of surface peat is removed, this community may be replaced by a wet flatwoods. If much of the surface layer is decreased, Baygalls will be invaded by willows and then change to a cypress-gum community. With recurrent fires, a shrub bog results (Clewell 1971, FNAI 1990).
In northeastern Florida, at the Timucuan Ecological and Historic Preserve, dead and dying Persea palustris indicate that these loblolly-bay forests are being affected by laurel wilt, which is caused by a vascular wilt fungus that is transmitted to species in the Lauraceae family via. the non-native redbay ambrosia beetle (Xyleborus glabratus).
Environmental Description: These forests occur in saturated, peat-filled seepage depressions usually located at the base of sandy slopes but also at the edges of floodplains or other flat areas with high water tables. The highly organic sands are often overlain by peat which erodes into hummocks and hollows; the peat substrate is very acidic with a pH between 3.0 and 4.5. Soils are usually saturated but flooding is infrequent. Water sources are adjacent slope seepage, perched water tables, and rainfall. Soil series of this community on the Apalachicola National Forest, Florida, are Rutlege and Ponzer. In North Carolina, soils include Croatan, Pamlico, and Dorovan (Clewell 1971, Jones 1981, FNAI 1990, Schafale and Weakley 1990).
Geographic Range: This association occurs on the Coastal Plain from Florida to North Carolina.
Nations: US
States/Provinces: FL, GA, NC, SC
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.684012
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G4
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 1 Forest & Woodland Class | C01 | 1 |
Subclass | 1.B Temperate & Boreal Forest & Woodland Subclass | S15 | 1.B |
Formation | 1.B.3 Temperate Flooded & Swamp Forest Formation | F026 | 1.B.3 |
Division | 1.B.3.Nb Southeastern North American Flooded & Swamp Forest Division | D062 | 1.B.3.Nb |
Macrogroup | 1.B.3.Nb.3 Sweetbay - Swamp Bay - Pond Pine Swamp Forest Macrogroup | M032 | 1.B.3.Nb.3 |
Group | 1.B.3.Nb.3.a Sweetbay - Loblolly-bay - Pond Pine Swamp Forest Group | G037 | 1.B.3.Nb.3.a |
Alliance | A0060 Sweetbay - Swamp Bay Swamp Forest Alliance | A0060 | 1.B.3.Nb.3.a |
Association | CEGL007044 Loblolly-bay - Sweetbay - Swamp Bay / Peatmoss species Swamp Forest | CEGL007044 | 1.B.3.Nb.3.a |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: < IIA2d. Bay Forest (Allard 1990)
< Sweetbay - Swamp Tupelo - Redbay: 104 (Eyre 1980)
< Sweetbay - Swamp Tupelo - Redbay: 104 (Eyre 1980)
- 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.
- Allard, D. J., K. M. Doyle, S. J. Landaal, and R. S. Martin. 1990. Community characterization abstracts for the southeastern United States. Unpublished manuscript. The Nature Conservancy, Southern Heritage Task Force, Chapel Hill, NC.
- 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.
- Clewell, A. F. 1971. The vegetation of the Apalachicola National Forest: An ecological perspective. Unpublished document. USDA Forest Service, Tallahassee, FL. 152 pp.
- Eyre, F. H., editor. 1980. Forest cover types of the United States and Canada. Society of American Foresters, Washington, DC. 148 pp.
- FNAI [Florida Natural Areas Inventory]. 2010a. Guide to the natural communities of Florida: 2010 edition. Florida Natural Areas Inventory, Tallahassee, FL. 228 pp. [https://fnai.org/naturalcommguide.cfm]
- GNHP [Georgia Natural Heritage Program]. 2018. Unpublished data. Georgia Natural Heritage Program, Wildlife Resources Division, Georgia Department of Natural Resources, Social Circle.
- Jones, R. H. 1981. A classification of lowland forests in the northern coastal plain of South Carolina. M.S. thesis, Clemson University, Clemson, SC.
- Kologiski, R. L. 1977. The phytosociology of the Green Swamp, North Carolina. North Carolina Agricultural Experiment Station. Bulletin No. 250. 101 pp.
- 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.
- 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.
- Wolfe, S. H., editor. 1990. An ecological characterization of the Florida Springs Coast: Pithlachascotee to Waccasassa rivers. USDI Fish & Wildlife Service, Biological Report 90(21). Slidell, LA. 323 pp.