Difference between revisions of "Ruellia caroliniensis"
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==Distribution== | ==Distribution== | ||
| − | ''R. caroliniensis'' is vulnerable to soil disturbances and is an indicator of native longleaf pine sites in southwestern Georgia. <ref name="K04"> Kirkman, L.K., K.L. Coffey, R.J. Mitchell, and E.B. Moser. 2004. Ground Cover Recovery Patterns and Life-History Traits: Implications for Restoration Obstacles and Opportunities in a Species-Rich Savanna. Journal of Ecology 92:409-421 </ref> | + | ''R. caroliniensis'' is vulnerable to soil disturbances and is an indicator of native longleaf pine sites in southwestern Georgia.<ref name="K04"> Kirkman, L.K., K.L. Coffey, R.J. Mitchell, and E.B. Moser. 2004. Ground Cover Recovery Patterns and Life-History Traits: Implications for Restoration Obstacles and Opportunities in a Species-Rich Savanna. Journal of Ecology 92:409-421 </ref> |
==Ecology== | ==Ecology== | ||
===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.--> | ||
| − | In the Coastal Plain in Florida and Georgia, ''R. caroliniensis'' can be found in the edges of wooded floodplains, mesic hardwood floodplains, drying sand of open woodlands, flatwoods, sandy alluvial banks, shallow marshes, and on bluffs along the Apalachicola River.<ref name="FSU Herbarium">Florida State University Robert K. Godfrey Herbarium database. URL: [http://herbarium.bio.fsu.edu http://herbarium.bio.fsu.edu]. Last accessed: July 2015. Collectors: Lisa Keppner, Ed Keppner, Loran C. Anderson, R.K. Godfrey, Cecil R Slaughter, Jimmy Meeks, R. Komarek, R. A. Norris. States and Counties: Florida: Bay, Dixie, Franklin, Gadsden, Leon, Liberty, Marion, Okaloosa, Washington. Georgia: Grady. Compiled by Tall Timbers Research Station and Land Conservancy.</ref> Soils include sandy loams, sand, and loamy sand.<ref name="FSU Herbarium"/> Associated species include oak, hickory, dogwood, pine, juniper and magnolia.<ref name="FSU Herbarium"/> | + | In the Coastal Plain in Florida and Georgia, ''R. caroliniensis'' can be found in the edges of wooded floodplains, mesic hardwood floodplains, drying sand of open woodlands, flatwoods, sandy alluvial banks, shallow marshes, and on bluffs along the Apalachicola River.<ref name="FSU Herbarium">Florida State University Robert K. Godfrey Herbarium database. URL: [http://herbarium.bio.fsu.edu http://herbarium.bio.fsu.edu]. Last accessed: July 2015. Collectors: Lisa Keppner, Ed Keppner, Loran C. Anderson, R.K. Godfrey, Cecil R Slaughter, Jimmy Meeks, R. Komarek, R. A. Norris. States and Counties: Florida: Bay, Dixie, Franklin, Gadsden, Leon, Liberty, Marion, Okaloosa, Washington. Georgia: Grady. Compiled by Tall Timbers Research Station and Land Conservancy.</ref> Soils include sandy loams, sand, and loamy sand.<ref name="FSU Herbarium"/> |
| + | |||
| + | Associated species include oak, hickory, dogwood, pine, juniper and magnolia.<ref name="FSU Herbarium"/> | ||
| + | |||
| + | ''R. caroliniensis'' became absent in response to military training in west Georgia pinelands.<ref>Dale, V.H., S.C. Beyeler, and B. Jackson. (2002). Understory vegetation indicators of anthropogenic disturbance in longleaf pine forests at Fort Benning, Georgia, USA. Ecological Indicators 1(3):155-170.</ref> It became absent or decreased its occurrence in response to disturbance by agriculture in southwest Georgia.<ref>Hedman, C.W., S.L. Grace, and S.E. King. (2000). Vegetation composition and structure of southern coastal plain pine forests: an ecological comparison. Forest Ecology and Management 134:233-247.</ref><ref>Kirkman, L.K., K.L. Coffey, R.J. Mitchell, and E.B. Moser. Ground Cover Recovery Patterns and Life-History Traits: Implications for Restoration Obstacles and Opportunities in a Species-Rich Savanna. (2004). Journal of Ecology 92(3):409-421.</ref> It has shown resistance to regrowth in these habitats after being disturbed by these practices. | ||
| + | |||
| + | However, this species has also increased its occurrence in response to disturbance by agriculture in other areas of southwest Georgia pinewoods. It has shown regrowth in reestablished pinewoods that were disturbed by agricultural practices.<ref>Ostertag, T. E. and K. M. Robertson. 2007. A comparison of native versus old-field vegetation in upland pinelands managed with frequent fire, South Georgia, USA. Tall Timbers Fire Ecology Conference Proceedings 23: 109-120.</ref> | ||
''Ruellia caroliniensis'' ssp. ''ciliosa'' is an indicator species for the North Florida Subxeric Sandhills community type as described in Carr et al. (2010).<ref>Carr, S.C., K.M. Robertson, and R.K. Peet. 2010. A vegetation classification of fire-dependent pinelands of Florida. Castanea 75:153-189.</ref> | ''Ruellia caroliniensis'' ssp. ''ciliosa'' is an indicator species for the North Florida Subxeric Sandhills community type as described in Carr et al. (2010).<ref>Carr, S.C., K.M. Robertson, and R.K. Peet. 2010. A vegetation classification of fire-dependent pinelands of Florida. Castanea 75:153-189.</ref> | ||
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===Seed dispersal=== | ===Seed dispersal=== | ||
| − | This species is thought to be dispersed by ants and/or explosive dehiscence. <ref>Kirkman, L. Katherine. Unpublished database of seed dispersal mode of plants found in Coastal Plain longleaf pine-grasslands of the Jones Ecological Research Center, Georgia.</ref> | + | This species is thought to be dispersed by ants and/or explosive dehiscence.<ref>Kirkman, L. Katherine. Unpublished database of seed dispersal mode of plants found in Coastal Plain longleaf pine-grasslands of the Jones Ecological Research Center, Georgia.</ref> |
<!--===Seed bank and germination===--> | <!--===Seed bank and germination===--> | ||
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It was observed resprouting one month after a fire in July of 1993.<ref name="Pav"> Pavon, M. L. 1995. Diversity and response of ground cover arthropod communities to different seasonal burns in longleaf pine forests. Tallahassee, Florida A&M University.</ref> | It was observed resprouting one month after a fire in July of 1993.<ref name="Pav"> Pavon, M. L. 1995. Diversity and response of ground cover arthropod communities to different seasonal burns in longleaf pine forests. Tallahassee, Florida A&M University.</ref> | ||
<!--===Pollination===--> | <!--===Pollination===--> | ||
| − | <!--=== | + | <!--===Herbivory and toxicology===<!--Common herbivores, granivory, insect hosting, poisonous chemicals, allelopathy, etc--> |
<!--===Diseases and parasites===--> | <!--===Diseases and parasites===--> | ||
| − | ==Conservation and | + | ==Conservation, cultivation, and restoration== |
| − | == | + | ==Cultural use== |
==Photo Gallery== | ==Photo Gallery== | ||
<gallery widths=180px> | <gallery widths=180px> | ||
Latest revision as of 10:33, 15 July 2022
| Ruellia caroliniensis | |
|---|---|
| |
| Photo taken by Gil Nelson | |
| Scientific classification | |
| Kingdom: | Plantae |
| Division: | Magnoliophyta – Flowering plants |
| Class: | Magnoliopsida – Dicotyledons |
| Order: | Scrophulariales |
| Family: | Acanthaceae |
| Genus: | Ruellia |
| Species: | R. caroliniensis |
| Binomial name | |
| Ruellia caroliniensis (J.F. Gmel.) Steud. | |
| |
| Natural range of Ruellia caroliniensis from USDA NRCS Plants Database. | |
Common name: Carolina wild petunia
Contents
Taxonomic notes
Synonyms: none
Varieties: Ruellia caroliniensis var. caroliniensis; R. caroliniensis var. typica; R. caroliniensis var. cheloniformis Fernald; R. caroliniensis var. dentata (Nees) Fernald; R. caroliniensis var. membranacea Fernald; R. caroliniensis var. nanella Fernald; R. caroliniensis var. salicina Fernald; R. caroliniensis var. semicalva Fernald; R. caroliniensis ssp. caroliniensis var. caroliniensis; R. parviflora (Nees) Britton
Description
R. caroliniensis is a small perennial varying 31 to 52 centimeters tall with oval leaves 6.7 to 7.5 centimeters long. The bluish-purple flowers bloom in early spring until late summer with seed capsules 0.4 centimeters wide and 1.3 centimeters long with brown seeds enclosed.[1]
"Perennial herbs. Leaves opposite, acute or obtuse, entire or undulate, base cuneate to attenuate, sessile or petiolate. Flowers in dense glomerules or in open cymes. Calyx tube short, lobes 5, elongate; corolla blue or rarely pink, funnel form, with tube, open throat, and 5 subequal lobes; stamens 4, included, anther locules parallel; stigmas 2-cleft. Capsules brown or yellow brown, compressed, ellipsoid-obovoid; seeds several, brown or gray."[2]
"Pubescent perennial, 1-6 dm tall. Leaves ovate, lanceolate, or elliptic, to 1-cm long and 4.5 cm wide, pubescent or glabrate, petioles to 12 mm long. Flowers in sessile or subsessile glomerules at middle and upper nodes. Calyx lobes usually hirsute, linear-setaceous, 15-22 mm long, less than 2 mm wide; corolla 2.5-4.5 cm long, tube longer than throat, lobes 5-15 mm long; ovary pubescent. Capsules usually glabrous, 12-16 mm long, ca. 5 mm broad; seeds brown, 2-2.5 mm broad."[2]
Distribution
R. caroliniensis is vulnerable to soil disturbances and is an indicator of native longleaf pine sites in southwestern Georgia.[3]
Ecology
Habitat
In the Coastal Plain in Florida and Georgia, R. caroliniensis can be found in the edges of wooded floodplains, mesic hardwood floodplains, drying sand of open woodlands, flatwoods, sandy alluvial banks, shallow marshes, and on bluffs along the Apalachicola River.[4] Soils include sandy loams, sand, and loamy sand.[4]
Associated species include oak, hickory, dogwood, pine, juniper and magnolia.[4]
R. caroliniensis became absent in response to military training in west Georgia pinelands.[5] It became absent or decreased its occurrence in response to disturbance by agriculture in southwest Georgia.[6][7] It has shown resistance to regrowth in these habitats after being disturbed by these practices.
However, this species has also increased its occurrence in response to disturbance by agriculture in other areas of southwest Georgia pinewoods. It has shown regrowth in reestablished pinewoods that were disturbed by agricultural practices.[8]
Ruellia caroliniensis ssp. ciliosa is an indicator species for the North Florida Subxeric Sandhills community type as described in Carr et al. (2010).[9]
Phenology
R. caroliniensis has been observed to flower from April to September with peak inflorescence in May.[4][10]
Seed dispersal
This species is thought to be dispersed by ants and/or explosive dehiscence.[11]
Fire ecology
It was observed resprouting one month after a fire in July of 1993.[12]
Conservation, cultivation, and restoration
Cultural use
Photo Gallery
References and notes
- ↑ Wilson, Sandra B. and P. Chris Wilson. 2004. Growth and Development of the Native Ruellia caroliniensis and Invasive Ruellia tweediana. HortScience 39:1015-1019.
- ↑ 2.0 2.1 Radford, Albert E., Harry E. Ahles, and C. Ritchie Bell. Manual of the Vascular Flora of the Carolinas. 1964, 1968. The University of North Carolina Press. 656. Print.
- ↑ Kirkman, L.K., K.L. Coffey, R.J. Mitchell, and E.B. Moser. 2004. Ground Cover Recovery Patterns and Life-History Traits: Implications for Restoration Obstacles and Opportunities in a Species-Rich Savanna. Journal of Ecology 92:409-421
- ↑ 4.0 4.1 4.2 4.3 Florida State University Robert K. Godfrey Herbarium database. URL: http://herbarium.bio.fsu.edu. Last accessed: July 2015. Collectors: Lisa Keppner, Ed Keppner, Loran C. Anderson, R.K. Godfrey, Cecil R Slaughter, Jimmy Meeks, R. Komarek, R. A. Norris. States and Counties: Florida: Bay, Dixie, Franklin, Gadsden, Leon, Liberty, Marion, Okaloosa, Washington. Georgia: Grady. Compiled by Tall Timbers Research Station and Land Conservancy.
- ↑ Dale, V.H., S.C. Beyeler, and B. Jackson. (2002). Understory vegetation indicators of anthropogenic disturbance in longleaf pine forests at Fort Benning, Georgia, USA. Ecological Indicators 1(3):155-170.
- ↑ Hedman, C.W., S.L. Grace, and S.E. King. (2000). Vegetation composition and structure of southern coastal plain pine forests: an ecological comparison. Forest Ecology and Management 134:233-247.
- ↑ Kirkman, L.K., K.L. Coffey, R.J. Mitchell, and E.B. Moser. Ground Cover Recovery Patterns and Life-History Traits: Implications for Restoration Obstacles and Opportunities in a Species-Rich Savanna. (2004). Journal of Ecology 92(3):409-421.
- ↑ Ostertag, T. E. and K. M. Robertson. 2007. A comparison of native versus old-field vegetation in upland pinelands managed with frequent fire, South Georgia, USA. Tall Timbers Fire Ecology Conference Proceedings 23: 109-120.
- ↑ Carr, S.C., K.M. Robertson, and R.K. Peet. 2010. A vegetation classification of fire-dependent pinelands of Florida. Castanea 75:153-189.
- ↑ Nelson, G. PanFlora: Plant data for the eastern United States with emphasis on the Southeastern Coastal Plains, Florida, and the Florida Panhandle. www.gilnelson.com/PanFlora/ Accessed: 13 DEC 2016
- ↑ Kirkman, L. Katherine. Unpublished database of seed dispersal mode of plants found in Coastal Plain longleaf pine-grasslands of the Jones Ecological Research Center, Georgia.
- ↑ Pavon, M. L. 1995. Diversity and response of ground cover arthropod communities to different seasonal burns in longleaf pine forests. Tallahassee, Florida A&M University.
