Difference between revisions of "Smilax auriculata"

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==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, ''S. auriculata'' can be found bordering mesic woodlands, longleaf pine turkey oak sand ridges (FSU Herbarium), palmetto flatwoods (FSU Herbarium; <ref name=olano> Olano, J. M., E. S. Menges, et al. (2006). "Carbohydrate storage in five resprouting Florida scrub plants across a fire chronosequence." New Phytologist 170: 99-105.
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In the Coastal Plain, specifically in Florida and Georgia, ''S. auriculata'' can be found bordering mesic woodlands, longleaf pine turkey oak sand ridges (FSU Herbarium), palmetto flatwoods (FSU Herbarium; <ref name=olano> Olano, J. M., E. S. Menges, et al. (2006). "Carbohydrate storage in five resprouting Florida scrub plants across a fire chronosequence." New Phytologist 170: 99-105.
</ref>), oak-saw palmetto scrubs (Foster and Schmalzer 2003), sandhill communities (FSU Herbarium; <ref name=rein> 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.</ref>), xeric longleaf pine woodlands (Peet and Allard 1993), and unburned scrubby flatwoods. <ref name=menges1995> Menges, E. and N. Kohfeldt (1995). "Life History Strategies of Florida Scrub Plants in Relation to Fire." Bulletin of the Torrey Botanical Club 122(4): 282-297</ref> It can also be found along railroads, powerline corridors, and disturbed longleaf pine restoration sites (FSU Herbarium). Soil types include loamy sand (FSU herbarium; Foster and Schmalzer 2003) and sandy, siliceous, hyperthermic Ultic haplaquod of the Pomona series. <ref name=moore> Moore, W. H., B. F. Swindel, et al. (1982). "Vegetative response to prescribed fire in a north Florida flatwoods forest." Journal of Range Management 35: 386-389.</ref> In habitats that include ''Pinus palustris, Quercus laevis, Q. incana, Sporobolus junceus'' and ''Licania michauxii'', ''S. auriculata'' accounts for most of the groundcover density. <ref name=prov> Provencher, L. M., B. J. Herring, et al. (2001). "Effects of hardwood reduction techniques on longleaf pine sandhill vegetation in northwest Florida." Restoration Ecology 9: 13-27.</ref>
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</ref>), oak-saw palmetto scrubs<ref name=foster> Foster, Tammy E., Paul A. Schmalzer. (2003). "The effect of season of fire on the recovery of Florida scrub". Dynamac Corporation, Kennedy Space Center, Florida. 2B.7. </ref>, sandhill communities (FSU Herbarium; <ref name=rein> 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.</ref>), xeric longleaf pine woodlands (Peet and Allard 1993), and unburned scrubby flatwoods. <ref name=menges1995> Menges, E. and N. Kohfeldt (1995). "Life History Strategies of Florida Scrub Plants in Relation to Fire." Bulletin of the Torrey Botanical Club 122(4): 282-297</ref> It can also be found along railroads, powerline corridors, and disturbed longleaf pine restoration sites (FSU Herbarium). Soil types include loamy sand (FSU herbarium; <ref name=foster/>) and sandy, siliceous, hyperthermic Ultic haplaquod of the Pomona series. <ref name=moore> Moore, W. H., B. F. Swindel, et al. (1982). "Vegetative response to prescribed fire in a north Florida flatwoods forest." Journal of Range Management 35: 386-389.</ref> In habitats that include ''Pinus palustris, Quercus laevis, Q. incana, Sporobolus junceus'' and ''Licania michauxii'', ''S. auriculata'' accounts for most of the groundcover density. <ref name=prov> Provencher, L. M., B. J. Herring, et al. (2001). "Effects of hardwood reduction techniques on longleaf pine sandhill vegetation in northwest Florida." Restoration Ecology 9: 13-27.</ref>
  
 
===Phenology=== <!--Timing off flowering, fruiting, seed dispersal, and environmental triggers.  Cite PanFlora website if appropriate: http://www.gilnelson.com/PanFlora/ -->
 
===Phenology=== <!--Timing off flowering, fruiting, seed dispersal, and environmental triggers.  Cite PanFlora website if appropriate: http://www.gilnelson.com/PanFlora/ -->

Revision as of 12:32, 12 April 2016

Smilax auriculata
Smilax auriculata Gil.jpg
Photo taken by Gil Nelson
Scientific classification
Kingdom: Plantae
Division: Magnoliophyta – Flowering plants
Class: Liliopsida – Monocotyledons
Order: Liliales
Family: Smilacaceae
Genus: Smilax
Species: S. auriculata
Binomial name
Smilax auriculata
Walter
SMIL AURI dist.jpg
Natural range of Smilax auriculata from USDA NRCS Plants Database.

Common name: earleaf greenbrier

Taxonomic notes

Description

A description of Smilax auriculata is provided in The Flora of North America.

Distribution

Ecology

Habitat

In the Coastal Plain, specifically in Florida and Georgia, S. auriculata can be found bordering mesic woodlands, longleaf pine turkey oak sand ridges (FSU Herbarium), palmetto flatwoods (FSU Herbarium; [1]), oak-saw palmetto scrubs[2], sandhill communities (FSU Herbarium; [3]), xeric longleaf pine woodlands (Peet and Allard 1993), and unburned scrubby flatwoods. [4] It can also be found along railroads, powerline corridors, and disturbed longleaf pine restoration sites (FSU Herbarium). Soil types include loamy sand (FSU herbarium; [2]) and sandy, siliceous, hyperthermic Ultic haplaquod of the Pomona series. [5] In habitats that include Pinus palustris, Quercus laevis, Q. incana, Sporobolus junceus and Licania michauxii, S. auriculata accounts for most of the groundcover density. [6]

Phenology

Flowering has been observed in May and fruiting June through July (FSU Herbarium).

Seed dispersal

According to Kay Kirkman, a plant ecologist, this species disperses by being consumed by vertebrates (being assumed). [7]

Seed bank and germination

It can reproduce by resprouting, clonal spreading, and seeding.[4]

Fire ecology

It increases in abundance after fire.[4] Its rapid recovery post-fire can be attributed to large specialized storage organs. [1] However, it was figured out that S. auriculata decreased to almost nonexistent following a May fire, suggesting that season of burning is important for this species. [8]

Pollination

The following Hymenoptera families and species were observed visiting flowers of Smilax auriculata at Archbold Biological Station (Deyrup 2015): [9]

Apidae: Apis mellifera

Halictidae: Augochlora pura

Megachilidae: Coelioxys dolichos, Megachile mendica, M. xylocopoides

Deyrup (2002)observed these bees, Augochlora pura, Coelioxys dolichos, Megachile mendica, M. xylocopoides, Apis mellifera, Xylocopa micans, X. virginica krombeini, on S. auriculata. [10]

Use by animals

S. auriculata was found in 5.5% of the Gopherus polyphemus scat [11] therefore, the gopher tortoise serves as an agent of seed dispersal.

Diseases and parasites

Conservation and Management

Cultivation and restoration

Photo Gallery

References and notes

Florida State University Robert K. Godfrey Herbarium database. URL: http://herbarium.bio.fsu.edu. Last accessed: July 2015. Collectors: Loran C. Anderson, Robert K. Godfrey, Robert A. Norris, R. Komarek, Cindi Stewart, Cecil R Slaughter, Marc Minno, Bob Fewster, Lisa Keppner. States and Counties: Florida: Flagler, Franklin, Gadsden, Jackson, Leon, Wakulla, Washington. Georgia: Camden. Compiled by Tall Timbers Research Station and Land Conservancy.

  1. 1.0 1.1 Olano, J. M., E. S. Menges, et al. (2006). "Carbohydrate storage in five resprouting Florida scrub plants across a fire chronosequence." New Phytologist 170: 99-105.
  2. 2.0 2.1 Foster, Tammy E., Paul A. Schmalzer. (2003). "The effect of season of fire on the recovery of Florida scrub". Dynamac Corporation, Kennedy Space Center, Florida. 2B.7.
  3. 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.
  4. 4.0 4.1 4.2 Menges, E. and N. Kohfeldt (1995). "Life History Strategies of Florida Scrub Plants in Relation to Fire." Bulletin of the Torrey Botanical Club 122(4): 282-297
  5. Moore, W. H., B. F. Swindel, et al. (1982). "Vegetative response to prescribed fire in a north Florida flatwoods forest." Journal of Range Management 35: 386-389.
  6. Provencher, L. M., B. J. Herring, et al. (2001). "Effects of hardwood reduction techniques on longleaf pine sandhill vegetation in northwest Florida." Restoration Ecology 9: 13-27.
  7. Kay Kirkman, unpublished data, 2015.
  8. Greenberg, C. H. (2003). "Vegetation recovery and stand structure following a prescribed stand-replacement burn in sand pine scrub." Natural Areas Journal 23: 141-151.
  9. Deyrup, M.A. and N.D. 2015. Database of observations of Hymenoptera visitations to flowers of plants on Archbold Biological Station, Florida, USA.
  10. Deyrup, Mark., Jayanthi Edirisinghe, Beth Norden. (2002). "The diversity and floral hosts of bees at the Archbold Biological Station, Florida (Hymenoptera: Apoidea). Insecta Mundi. Vol. 16. No.1-3. Pages 87-102.
  11. Carlson, J. E., E. S. Menges, et al. (2003). "Seed dispersal by Gopherus polyphemus at Archbold Biological Station, Florida." Florida Scientist 66: 147-154.