Difference between revisions of "Galactia regularis"
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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.--> | ||
''Galactia regularis'' has been documented in open sand ridges, open cedar glades, dry prairies, dry upland woods, along rocky banks, scrub oak-wiregrass ridges, shell ridge in a brackish marsh, dry grassy scrub border of a cypress swamp, open oak-hickory woods of a bog boarder, and mature longleaf pine-wiregrass stand that is frequently burned (FSU Herbarium). | ''Galactia regularis'' has been documented in open sand ridges, open cedar glades, dry prairies, dry upland woods, along rocky banks, scrub oak-wiregrass ridges, shell ridge in a brackish marsh, dry grassy scrub border of a cypress swamp, open oak-hickory woods of a bog boarder, and mature longleaf pine-wiregrass stand that is frequently burned (FSU Herbarium). | ||
| − | It can be found in xeric areas with hot, wet summers and mild, dry winters | + | It can be found in xeric areas with hot, wet summers and mild, dry winters (Hawkes and Menges 2003) Pine sandhill communities (Downer 2012). |
| − | It can be found in shrubland | + | It can be found in shrubland (Hawkes and Menges 2003). |
At Heart Island Conservation area it has been recorded in pine flatwoods and at the edges of pond cypress wetlands (FSU Herbarium). Along the Apalachicola River East of Sneads, ''G. regularis'' was observed growing in an edge of a floodplain woodland on a natural levee (FSU Herbarium). | At Heart Island Conservation area it has been recorded in pine flatwoods and at the edges of pond cypress wetlands (FSU Herbarium). Along the Apalachicola River East of Sneads, ''G. regularis'' was observed growing in an edge of a floodplain woodland on a natural levee (FSU Herbarium). | ||
| Line 48: | Line 48: | ||
===Seed dispersal=== | ===Seed dispersal=== | ||
===Seed bank and germination=== | ===Seed bank and germination=== | ||
| − | Maximum germination was observed for G. regularis at the 80 degrees Celsius dry heat shock treatment. Wet heat (boiling water) treatments, however, resulted in 100% mortality of seeds | + | Maximum germination was observed for G. regularis at the 80 degrees Celsius dry heat shock treatment. Wet heat (boiling water) treatments, however, resulted in 100% mortality of seeds (Bolin 2009). |
| − | Soil scarification seems to impede germination | + | Soil scarification seems to impede germination(Mou et. al 2005). It reproduces by resprouting after fire(Reinhart and Menges 2004). |
===Fire ecology=== <!--Fire tolerance, fire dependence, adaptive fire responses--> | ===Fire ecology=== <!--Fire tolerance, fire dependence, adaptive fire responses--> | ||
In a field study of vegetation change in Florida scrub, G. regularis cover increased after fire.<ref>Weekley, C.W. and E.S. Menges. 2003. Species and vegetation responses to prescribed fire in a long-unburned, endemic-rich Lake Wales ridge scrub. J. Torrey Bot. Soc. 130: 265-282. Bolin, J. F. (2009). "Heat shock germination responses of three eastern North American temperate species." Castanea 74: 160-167.</ref> However, this increase may not be the direct result of fire. Heat shock germination may play a role in its post-fire recruitment.<ref name="Bolin 2009"/> The amount of G. regularis decreased after a spring burn; decreased slightly after a summer burn; and increased in the control plots.<ref name="Cushwa et al 1970">Cushwa, C. T., M. Hopkins, et al. (1970). Response of legumes to prescribed burns in loblolly pine stands of the South Carolina Piedmont. Asheville, NC, USDA Forest Service, Research Note SE-140: 6.</ref> | In a field study of vegetation change in Florida scrub, G. regularis cover increased after fire.<ref>Weekley, C.W. and E.S. Menges. 2003. Species and vegetation responses to prescribed fire in a long-unburned, endemic-rich Lake Wales ridge scrub. J. Torrey Bot. Soc. 130: 265-282. Bolin, J. F. (2009). "Heat shock germination responses of three eastern North American temperate species." Castanea 74: 160-167.</ref> However, this increase may not be the direct result of fire. Heat shock germination may play a role in its post-fire recruitment.<ref name="Bolin 2009"/> The amount of G. regularis decreased after a spring burn; decreased slightly after a summer burn; and increased in the control plots.<ref name="Cushwa et al 1970">Cushwa, C. T., M. Hopkins, et al. (1970). Response of legumes to prescribed burns in loblolly pine stands of the South Carolina Piedmont. Asheville, NC, USDA Forest Service, Research Note SE-140: 6.</ref> | ||
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==Photo Gallery== | ==Photo Gallery== | ||
==References and notes== | ==References and notes== | ||
| + | Bolin, J. F. (2009). "Heat shock germination responses of three eastern North American temperate species." Castanea 74: 160-167. | ||
| + | |||
Deyrup, M.A. and N.D. 2015. Database of observations of Hymenoptera visitations to flowers of plants on Archbold Biological Station, Florida, USA. | Deyrup, M.A. and N.D. 2015. Database of observations of Hymenoptera visitations to flowers of plants on Archbold Biological Station, Florida, USA. | ||
| + | |||
| + | Downer, M. R. (2012). Plant species richness and species area relationships in a Florida sandhill community. Integrative Biology. Ann Arbor, MI, University of South Florida. M.S.: 52. | ||
Florida State University Robert K. Godfrey Herbarium database. URL: [http://herbarium.bio.fsu.edu http://herbarium.bio.fsu.edu]. Last accessed: July 2015 Collectors: Loran C. Anderson, H. E. Ahles, Tom Barnes, Michael B. Brooks, Robert W. Simons, Dianna Hall, R. Kral, R. K. Godfrey, Sidney McDaniel, R. A. Norris, H. R. Reed, Cecil R. Slaughter, Frankie Snow, A. E. Redford, C. Simon, A. A. Eaton, Robert L. Lazor, Bruce Hansen, JoAnn Hansen, W. A. Silveus, A. F. Clewell, Robert Blaisdell, O. Lakela, George R. Cooley, Richard J. Eaton, Daniel B. Ward, Paul O. Schallert, A. H. Curtiss States and Counties: Florida: Bay, Brevard, Clay, Dixie, Duval, Escambia, Franklin, Flagler, Gadsden, Hillsborough, Jackson, Jefferson, Leon, Levy, Liberty, Madison, Nassau, Osceola, Putnam, Sarasota, St. Johns, Taylor, Wakulla, Washington. Georgia: Camden, Coffee, Grady. Mississippi: Pearl River, Oktibbeha. North Carolina: Alexander. South Carolina: Hampton. Virginia: Pulaski. Compiled by Tall Timbers Research Station and Land Conservancy. | Florida State University Robert K. Godfrey Herbarium database. URL: [http://herbarium.bio.fsu.edu http://herbarium.bio.fsu.edu]. Last accessed: July 2015 Collectors: Loran C. Anderson, H. E. Ahles, Tom Barnes, Michael B. Brooks, Robert W. Simons, Dianna Hall, R. Kral, R. K. Godfrey, Sidney McDaniel, R. A. Norris, H. R. Reed, Cecil R. Slaughter, Frankie Snow, A. E. Redford, C. Simon, A. A. Eaton, Robert L. Lazor, Bruce Hansen, JoAnn Hansen, W. A. Silveus, A. F. Clewell, Robert Blaisdell, O. Lakela, George R. Cooley, Richard J. Eaton, Daniel B. Ward, Paul O. Schallert, A. H. Curtiss States and Counties: Florida: Bay, Brevard, Clay, Dixie, Duval, Escambia, Franklin, Flagler, Gadsden, Hillsborough, Jackson, Jefferson, Leon, Levy, Liberty, Madison, Nassau, Osceola, Putnam, Sarasota, St. Johns, Taylor, Wakulla, Washington. Georgia: Camden, Coffee, Grady. Mississippi: Pearl River, Oktibbeha. North Carolina: Alexander. South Carolina: Hampton. Virginia: Pulaski. Compiled by Tall Timbers Research Station and Land Conservancy. | ||
Graham, E. H. (1941). Legumes for erosion control and wildlife. Washington, USDA | Graham, E. H. (1941). Legumes for erosion control and wildlife. Washington, USDA | ||
| + | |||
| + | Hawkes, C. V. and E. S. Menges (2003). "Effects of lichens on seedling emergence in a xeric Florida shrubland." Southeastern Naturalist 2: 223-234. | ||
Mou, P., R. H. Jones, et al. (2005). "Regeneration strategies, disturbance and plant interactions as organizers of vegetation spatial patterns in a pine forest." Landscape Ecology 20: 971-987. | Mou, P., R. H. Jones, et al. (2005). "Regeneration strategies, disturbance and plant interactions as organizers of vegetation spatial patterns in a pine forest." Landscape Ecology 20: 971-987. | ||
| + | |||
| + | Reinhart, K. O. and E. S. Menges (2004). "Effects of re-introducing fire to a central Florida sandhill community." Applied Vegetation Science 7: 141-150. | ||
Revision as of 14:38, 16 September 2015
| Galactia regularis | |
|---|---|
| |
| Photo was taken by Gil Nelson | |
| Scientific classification | |
| Kingdom: | Plantae |
| Division: | Magnoliophyta - Flowering plants |
| Class: | Magnoliopsida – Dicotyledons |
| Order: | Fabales |
| Family: | Fabaceae ⁄ Leguminosae |
| Genus: | Galactia |
| Species: | G. regularis |
| Binomial name | |
| Galactia regularis (L.) Britton, Sterns & Poggenb. | |
| |
| Natural range of Galactia regularis from USDA NRCS Plants Database. | |
Common name: eastern milkpea
Contents
Description
Is strongly paraheliotropic,[1]
G. regularis is a prostrate perennial with showy violet-purple flowers, frequently found climbing over bushes (Graham 1941). Stems have been observed to twine on low shrubs (FSU Herbarium). It has been documented as a prostrate structure (FSU Herbarium).
Distribution
It occurs in pinelands and sandy woods from New York to Florida and Mississippi (Graham 1941). Occurs in Pinus elliottii plantation in South Carolina (Mou et. al 2005).
Ecology
Habitat
Galactia regularis has been documented in open sand ridges, open cedar glades, dry prairies, dry upland woods, along rocky banks, scrub oak-wiregrass ridges, shell ridge in a brackish marsh, dry grassy scrub border of a cypress swamp, open oak-hickory woods of a bog boarder, and mature longleaf pine-wiregrass stand that is frequently burned (FSU Herbarium). It can be found in xeric areas with hot, wet summers and mild, dry winters (Hawkes and Menges 2003) Pine sandhill communities (Downer 2012). It can be found in shrubland (Hawkes and Menges 2003).
At Heart Island Conservation area it has been recorded in pine flatwoods and at the edges of pond cypress wetlands (FSU Herbarium). Along the Apalachicola River East of Sneads, G. regularis was observed growing in an edge of a floodplain woodland on a natural levee (FSU Herbarium).
In areas of human impact, G. regularis has been found growing entwined with Galactia volubilis and Rhynchosia difformis(FSU Herbarium). Recorded populations have been found at Miami Biscayne Dog Track and an area of clay with sandstone that had been recently cleared and bulldozed (FSU Herbarium).
Soils range from sand to sandy loam.
Species of Elephantopus, Yucca, bahia grass, centipede grass, Galactia volubilis and Rhynchosia difformis have been associated with G. regularis (FSU Herbarium).
Phenology
Flowers June through November (FSU Herbarium).
Seed dispersal
Seed bank and germination
Maximum germination was observed for G. regularis at the 80 degrees Celsius dry heat shock treatment. Wet heat (boiling water) treatments, however, resulted in 100% mortality of seeds (Bolin 2009). Soil scarification seems to impede germination(Mou et. al 2005). It reproduces by resprouting after fire(Reinhart and Menges 2004).
Fire ecology
In a field study of vegetation change in Florida scrub, G. regularis cover increased after fire.[2] However, this increase may not be the direct result of fire. Heat shock germination may play a role in its post-fire recruitment.[3] The amount of G. regularis decreased after a spring burn; decreased slightly after a summer burn; and increased in the control plots.[4] A total of 24 plants in four new quadrants were recruited postburn study in the Florida scrub – Lake Wales Ridge area.[5] “Results from previous studies[6] indicate that leguminous plants and seed respond best to “hot” f i r e s - - i . e., those in which a high proportion of the ground fuel is consumed. Laboratory tests[7] have also shown that seed from several leguminous species germinate best after scarification with moist heat at temperatures near 80” C., a situation requiring a hot fire. The response of the leguminous plants and seed in this study, therefore, would probably have been greater if the pine stands had been burned with more intense fires. Nevertheless, further work will be necessary before we can make final conclusions about the value of prescribed burning to quail and other wildlife in the 2.5 million acres of pine in the South Carolina Piedmont.”[4] As an herbaceous vine, the amount of groundcover of G. regularis increased slightly when the area has not been burned (controlled treatment). The amount of groundcover decreased from ~58 to 23% after a burn. (Michelle’s understanding that the G. regularis had a higher population when the area was burned previously before the experiments were conducted).[8]
Pollination
The following Hymenoptera families and species were observed visiting flowers of Galactia regularis at Archbold Biological Station (Deyrup 2015):
Apidae: Apis mellifera, Bombus impatiens, Svastra atripes
Halictidae: Augochlorella aurata, Augochloropsis metallica, A. sumptuosa, Nomia maneei
Megachilidae: Anthidiellum notatum rufomaculatum, A. perplexum, Anthidium maculifrons, Coelioxys germana, C. sayi, Megachile albitarsis, M. brevis pseudobrevis, M. brimleyi, M. deflexa, M. exilis parexilis, M. georgica, M. integra, M. mendica, M. petulans
Sphecidae: Trypargilum clavatum johannis
Vespidae: Stenodynerus fundatiformis
Use by animals
On occasion, occurred in White-tailed deer’s diet.[9] “Seeds have been found in stomachs of the bobwhite, for which it is considered an important food.”[10]
Diseases and parasites
G. regularis reposnded moderately resistant to a root-knotnematodes study. A nematode, M. incognita, showed an immune response to the root galls and egg masses in the 2004 study but only a highly resistant response in 2001.[11]
Conservation and Management
Cultivation and restoration
Photo Gallery
References and notes
Bolin, J. F. (2009). "Heat shock germination responses of three eastern North American temperate species." Castanea 74: 160-167.
Deyrup, M.A. and N.D. 2015. Database of observations of Hymenoptera visitations to flowers of plants on Archbold Biological Station, Florida, USA.
Downer, M. R. (2012). Plant species richness and species area relationships in a Florida sandhill community. Integrative Biology. Ann Arbor, MI, University of South Florida. M.S.: 52.
Florida State University Robert K. Godfrey Herbarium database. URL: http://herbarium.bio.fsu.edu. Last accessed: July 2015 Collectors: Loran C. Anderson, H. E. Ahles, Tom Barnes, Michael B. Brooks, Robert W. Simons, Dianna Hall, R. Kral, R. K. Godfrey, Sidney McDaniel, R. A. Norris, H. R. Reed, Cecil R. Slaughter, Frankie Snow, A. E. Redford, C. Simon, A. A. Eaton, Robert L. Lazor, Bruce Hansen, JoAnn Hansen, W. A. Silveus, A. F. Clewell, Robert Blaisdell, O. Lakela, George R. Cooley, Richard J. Eaton, Daniel B. Ward, Paul O. Schallert, A. H. Curtiss States and Counties: Florida: Bay, Brevard, Clay, Dixie, Duval, Escambia, Franklin, Flagler, Gadsden, Hillsborough, Jackson, Jefferson, Leon, Levy, Liberty, Madison, Nassau, Osceola, Putnam, Sarasota, St. Johns, Taylor, Wakulla, Washington. Georgia: Camden, Coffee, Grady. Mississippi: Pearl River, Oktibbeha. North Carolina: Alexander. South Carolina: Hampton. Virginia: Pulaski. Compiled by Tall Timbers Research Station and Land Conservancy.
Graham, E. H. (1941). Legumes for erosion control and wildlife. Washington, USDA
Hawkes, C. V. and E. S. Menges (2003). "Effects of lichens on seedling emergence in a xeric Florida shrubland." Southeastern Naturalist 2: 223-234.
Mou, P., R. H. Jones, et al. (2005). "Regeneration strategies, disturbance and plant interactions as organizers of vegetation spatial patterns in a pine forest." Landscape Ecology 20: 971-987.
Reinhart, K. O. and E. S. Menges (2004). "Effects of re-introducing fire to a central Florida sandhill community." Applied Vegetation Science 7: 141-150.
- ↑ KMR observation at Pebble Hill Plantation, Georgia in July.
- ↑ Weekley, C.W. and E.S. Menges. 2003. Species and vegetation responses to prescribed fire in a long-unburned, endemic-rich Lake Wales ridge scrub. J. Torrey Bot. Soc. 130: 265-282. Bolin, J. F. (2009). "Heat shock germination responses of three eastern North American temperate species." Castanea 74: 160-167.
- ↑ Cite error: Invalid
<ref>tag; no text was provided for refs namedBolin 2009 - ↑ 4.0 4.1 Cushwa, C. T., M. Hopkins, et al. (1970). Response of legumes to prescribed burns in loblolly pine stands of the South Carolina Piedmont. Asheville, NC, USDA Forest Service, Research Note SE-140: 6.
- ↑ Weekley, C.W. and E.S. Menges. 2003. Species and vegetation responses to prescribed fire in a long-unburned, endemic-rich Lake Wales ridge scrub. J. Torrey Bot. Soc. 130: 265-282.
- ↑ Cushwa, C. T., Czuhai, Eugene, Cooper, R. W., and Julian, W. H. 1969. Burning clearcut openings in Ioblolly pine to improve wildlife habitat. Ga. Forest Res. Count. Res. Pap. 61, 5 pp. Cushwa, C. T. and Redd, J. B. 1966. One prescribed burn and its effects on habitat of the Powhatan Game Management Area. Southeast. Forest Exp. %a., U. S. Forest Serv. Res. Note SE-61, 2 pp.
- ↑ Cushwa, C. T., Martin, R. E., and Miller, R. L. 1968. The effects of fire on seed germination. J. Range Manage. 21: 250-254. M a r t i n , R . E., a n d C u s h w a , C . T. 1966. Effects of heat and moisture on leguminous seed. Fifth Annu. Tall Timbers Fire Ecol. Conf. Proc. 1966: 159-175.
- ↑ Reinhart, K. O. and E. S. Menges (2004). "Effects of re-introducing fire to a central Florida sandhill community." Applied Vegetation Science 7: 141-150.
- ↑ Gee, K. L., M. D. Porter, et al. (1994). White-tailed deer : their foods and management in the cross timbers. Ardmore, OK, Samuel Roberts Noble Foundation.
- ↑ Cite error: Invalid
<ref>tag; no text was provided for refs namedGraham 1941 - ↑ Quesenberry, K. H., J. M. Dampier, et al. (2008). "Response of native southeastern U.S. legumes to root-knot nematodes." Crop Science 48: 2274-2278.
