Difference between revisions of "Lespedeza angustifolia"
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===Habitat=== <!--Natural communities, human disturbed habitats, topography, hydrology, soils, light, fire regime requirements for removal of competition, etc.--> | ===Habitat=== <!--Natural communities, human disturbed habitats, topography, hydrology, soils, light, fire regime requirements for removal of competition, etc.--> | ||
| − | ''Lespedeza angustifolia'' habitats include sandhills, pine flatwoods, and oldfield pinelands, as well as dry pond margins and open flood plains on areas that are mesic to excessively well drained (FSU Herbarium). It has been strongly associated with hydric habitats (Hainds et. al 1990). | + | ''Lespedeza angustifolia'' habitats include sandhills, pine flatwoods, and oldfield pinelands, as well as dry pond margins and open flood plains on areas that are mesic to excessively well drained (FSU Herbarium). It has been strongly associated with hydric habitats (Hainds et. al 1990).This this association occurs because of a higher tolerance for periodically inudated soil conditions (Hainds et. al 1997). It has been documented to occur in dried up bottoms of sinkhole ponds (FSU Herbarium). Soils include sand and sandy loams, including Ultisols, Entisols, and dry Spodosols .<ref>Clewell, Andre. 2014. Personal observations</ref>. Other soil types includes red sandy clay hills and sandy peat (FSU Herbarium). Presence of ''Imperata cylindrica'' (cogan grass), an invasive plant found in the southeastern United States, did not deter the occurrence of ''L. angustifolia'' in plots that had been burned every 1 to 2 years in southeastern Mississippi (Brewer and Cralle 2003). In its natural habitat it requires frequent fire for persistence. It is primarily located in undisturbed sites and sometimes colonizes frequently burned old-field pinelands.<ref name="Clewell">Clewell, Andre. 2014. Personal observations. </ref> |
''L. angustifolia'' is prevalent along eroded roadsides and railroads (FSU Herbarium). | ''L. angustifolia'' is prevalent along eroded roadsides and railroads (FSU Herbarium). | ||
Revision as of 10:00, 17 September 2015
| Lespedeza angustifolia | |
|---|---|
| |
| Scientific classification | |
| Kingdom: | Plantae |
| Division: | Magnoliophyta - Flowering plants |
| Class: | Magnoliopsida – Dicotyledons |
| Order: | Fabales |
| Family: | Fabaceae ⁄ Leguminosae |
| Genus: | Lespedeza |
| Species: | L. angustifolia |
| Binomial name | |
| Lespedeza angustifolia (Pursh) Elliott | |
| |
| Natural range of Lespedeza angustifolia from USDA NRCS Plants Database. | |
Common name: narrowleaf lespedeza
Contents
Taxonomic notes
Description
Distribution
Ecology
Habitat
Lespedeza angustifolia habitats include sandhills, pine flatwoods, and oldfield pinelands, as well as dry pond margins and open flood plains on areas that are mesic to excessively well drained (FSU Herbarium). It has been strongly associated with hydric habitats (Hainds et. al 1990).This this association occurs because of a higher tolerance for periodically inudated soil conditions (Hainds et. al 1997). It has been documented to occur in dried up bottoms of sinkhole ponds (FSU Herbarium). Soils include sand and sandy loams, including Ultisols, Entisols, and dry Spodosols .[1]. Other soil types includes red sandy clay hills and sandy peat (FSU Herbarium). Presence of Imperata cylindrica (cogan grass), an invasive plant found in the southeastern United States, did not deter the occurrence of L. angustifolia in plots that had been burned every 1 to 2 years in southeastern Mississippi (Brewer and Cralle 2003). In its natural habitat it requires frequent fire for persistence. It is primarily located in undisturbed sites and sometimes colonizes frequently burned old-field pinelands.[2]
L. angustifolia is prevalent along eroded roadsides and railroads (FSU Herbarium).
Plants associated include Aristida, Ctenium, Andropogon, Sporobolus and Panicum hemitomon (FSU Herbarium).
Phenology
It blooms from September to November. Frequent where present by populations tend to be separated from one another.[2]
Seed dispersal
Seed bank and germination
Lespedeza and other legume species have the hard seed coat. Species with hard seed coats are likely capable of forming long-term persistent seed banks, and continuation of the buried seed bag portion of this study will yield long-term data on this subject (Coffey and Kirkman 2006). Although perennial species of longleaf pine ecosystems, such as Lespedeza, persist through frequent fire, fire exposes seeds in soil to higher temperature and high amplitudes of temperature fluctuation (Grime 1989) leading in some cases to germination (Coffey and Kirkman 2006).
Fire ecology
Frequent dormant season burning increased legume populations in southern pine forests, although fires during the growing season at the same frequency tended to reduce legume abundance (White et. al 1990).
Pollination
bee andLepidopteran pollinated in chasmogamous flowers afc
Use by animals
Diseases and parasites
Conservation and Management
Cultivation and restoration
Photo Gallery
References and notes
Brewer, J. S. and S. P. Cralle (2003). "Phosphorus addition reduces invasion of a longleaf pine savanna (southeastern USA) by a non-indigenous grass (Imperata cylindrica)." Plant Ecology 167: 237-245.
Coffey, K. L. and L. K. Kirkman (2006). "Seed germination strategies of species with restoration potential in a fire-maintained pine savanna." Natural Areas Journal 26: 289-299.
Florida State University Robert K. Godfrey Herbarium database. URL: http://herbarium.bio.fsu.edu. Last accessed: July 2015 Collectors:Loran C. Anderson, Wilson Baker, A. F. Clewell, James R. Coleman, Delzie Demaree, William B. Fox, J. P. Gillespie, Robert K. Godfrey, Gary R. Knight, R. Komarek, R. Kral, T. MacClendon, John Morrill, A. E. Radford, John K. Small States and Counties: Alabama: Baldwin. Florida: Franklin, Jackson, Jefferson, Leon, Liberty, Madison, Nassau, Wakulla, Washington. Georgia: Appling, Baker, Camden, Clinch, Grady, Lowndes, Miller, Seminole, Thomas, Walton, Wilcox. North Carolina: Cumberland, Harnett, Pitt. South Carolina: Sumter. Compiled by Tall Timbers Research Station and Land Conservancy.
Grime, J.P. 1989. Seed banks in ecological perspective. Pp. xv-xxii in M.A. Leck, V.T.Parker, and R.L. Simpson, eds., Ecology of Soil Seed Banks. Academic Press, San Diego, Calif.
Hainds, M. J., R. J. Mitchell, et al. (1999). "Distribution of native legumes (Leguminoseae) in frequently burned longleaf pine (Pinaceae)-wiregrass (Poaceae) ecosystems." American Journal of Botany 86: 1606-1614.
Hainds, M. J., R. J. Mitchell, et al. (1997). "Legume population dynamics in frequently burned longleaf pine-wiregrass fire ecosystem." Proceedings Longleaf Alliance Conference: Longleaf Alliance Report 1: 82-86.
