Difference between revisions of "Cyperus retrorsus"
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==Conservation and management== | ==Conservation and management== | ||
| + | This species is listed as endangered by the New York Department of Environmental Conservation Division of Land and Forests, and listed as extirpated by the Pennsylvania Department of Conservation and Natural Resources.<ref name= "USDA">USDA, NRCS. (2016). The PLANTS Database (http://plants.usda.gov, 25 April 2019). National Plant Data Team, Greensboro, NC 27401-4901 USA.</ref> | ||
==Cultivation and restoration== | ==Cultivation and restoration== | ||
Revision as of 10:18, 25 April 2019
| Cyperus retrorsus | |
|---|---|
| |
| Photo by Dwight K. Lauer, Auburn University, Bugwood.org | |
| Scientific classification | |
| Kingdom: | Plantae |
| Division: | Magnoliophyta - Flowering plants |
| Class: | Liliopsida – Monocotyledons |
| Order: | Poales |
| Family: | Cyperaceae |
| Genus: | Cyperus |
| Species: | C. retrorsus |
| Binomial name | |
| Cyperus retrorsus Chapm. | |
| |
| Natural range of Cyperus retrorsus from USDA NRCS Plants Database. | |
Common names: Pine Barren Flatsedge; Pineland Flatsedge
Contents
Taxonomic notes
Synonyms: Cyperus retrorsus Chapman var. retrorsus; C. torreyi Britton
Varieties: none
Description
A description of Cyperus retrorsus is provided in The Flora of North America. Cyperus retrorsus is a perennial graminoid. Most individuals are composed of 1-3 stems. [1]
Distribution
C. retrorsus is natively distributed from south New York south to Florida and west to Texas. It is mostly found within the Gulf Coastal Plain, but can also be found up to Kentucky and west to southeast Oklahoma.[2]
Ecology
Habitat
C. retrorsus requires wet summers and dry winters.[3] It also prefers higher light levels associated with open or semi-shaded conditions, and moist to wet sandy soils. [1] It has been observed growing in a variety of related soil types, including wet sand, moist sandy peat, moist loamy sand, drying sandy soil, drying loam, peat, and dry sterile sand. [1]
As such, this species can be found in or near wet habitat like pocosin communities,[4] lake shores, phosphate pools, marshes, lakeside sinkhole berms, drained bogs, river floodplains, seepage streams, and drying wetland depressions. [1] However, it also can be found in drier areas, including flatwoods communities,[5] and longleaf pine communities.[6] Additionally, it has been found in oak-hickory forests, grassy areas on islands, turkey oak sand ridges, sandhills, live oak hammocks, dried lake bottoms, pine flatwoods-savannas, old stabilized sand dunes, prairies, open scrub, and scrub barrens. [1]
Along with being found in natural community types, C. retrorsus has been found in disturbed habitat such as cleared floodplains, roadside ditches, railways, trail edges, clear-cuts, fallow fields, borrow pits, dredge spoils, former pine plantations, orange groves, longleaf pine restoration sites, and disturbed sandhill communities. [1]
Associated species include Paspalum notatum, Eupatorium mohrii, Rubus cuneifolius, Ludwigia maritima, Pityopsis, Solidago fistulosa, Aletris lutea, Eleusine, Dactyloctenium, Digitaria, Panicum, Rhynchospora fernaldii, R. fasicularis, Andropogon, Scleria reticularis, Trilisa, Liatris, Aristida, Andropogon, Bulbostylis, Clitoria, Juncus, Pteridium aquilinum, Cyperus filiculmis, Commelina erecta, Serenoa repens, Sagittaria graminea, Woodwardia virginica, Nyssa biflora, Acer rubrum, Liquidambar styraciflua, Rynchospora fernaldii, R. fascicularis, Carex longii, madien cane, and others. [1]
Phenology
Flowering has been observed in July through October. [1]
Seed dispersal
This species is thought to be dispersed by gravity. [7]
Seed bank and germination
It accounted for 29% of a late-summer Virginia pocosin seed bank.[4] It was also found viable in the seedbank in a pine flatwoods site in Florida after 8 years of fire exclusion[8] and in the seed bank of a longleaf pine community in the western panhandle region of Florida. [9]
Fire ecology
C. cyperus has been found in burned areas including recently burned slash pine-scrub flat, annually burned savanna, and frequently burned mature longleaf pine-wiregrass communities, indicating a level of fire tolerance. [1]
It responds best to a moderate-severity level burn. Recovery after fire is achieved by resprouting and seed.[3] Abundance was found to significantly decrease over 25 years after fire in a scrubby flatwoods, suggesting the significance of fire in its life history.[10]
Conservation and management
This species is listed as endangered by the New York Department of Environmental Conservation Division of Land and Forests, and listed as extirpated by the Pennsylvania Department of Conservation and Natural Resources.[11]
Cultivation and restoration
Photo Gallery
References and notes
- ↑ 1.0 1.1 1.2 1.3 1.4 1.5 1.6 1.7 1.8 Florida State University Robert K. Godfrey Herbarium database. URL: http://herbarium.bio.fsu.edu. Last accessed: June 2014. Collectors: S. W. Leonard, R.K. Godfrey, Angus Gholson, D. S. Correll, Helen B. Correll, Andre F. Clewell, Loran C. Anderson, Nancy Coile, S. W. Leonard, Richard Carter, Cecil R Slaughter, Travis MacClendon, Karen MacClendon, R. Kral, James P. Gillespie, A. H. Curtiss, O. Lakela, S. M. Tracy, Robert L. Lazor, K. Craddock Burks, R. R. Smith, Gary R. Knight, H. Kurz, Richard S. Mitchell, Grady W. Reinert, P. L. Redfearn, Jr., Allen G. Shuey, D. L. Martin, S. T. Cooper, Brenda Herring, Don Herring, William Reese, Bruce Hansen, JoAnn Hansen, Sidney McDaniel, D. B. Ward, R. A. Norris, Chris Cooksey, R. Komarek, Ann F. Johnson, Lisa Keppner, Michael Keys, and Paul Redfearn. States and Counties: Alabama: Geneva. Florida: Bay, Brevard, Calhoun, Charlotte, Clay, Collier, Columbia, Duval, Escambia, Franklin, Gadsden, Gilchrist, Gulf, Highlands, Hillsborough, Indian River, Jackson, Jefferson, Lake, Lamar, Leon, Liberty, Madison, Manatee, Marion, Okaloosa, Orange, Osceola, Pasco, Polk, Putnam, Sarasota, Sumter, Taylor, Wakulla, Walton, and Washington. Georgia: Grady, Liberty, and Thomas.
- ↑ Weakley, A. S. (2015). Flora of the Southern and Mid-Atlantic States. Chapel Hill, NC, University of North Carolina Herbarium.
- ↑ 3.0 3.1 Freeman, J. E. and L. N. Kobziar (2011). "Tracking postfire successional trajectories in a plant community adapted to high-severity fire." Ecological Applications 21: 61-74.
- ↑ 4.0 4.1 Bolin, J. F. (2007). "Seed bank response to wet heat and the vegetation structure of a Virginia pocosin." Journal of the Torrey Botanical Society 134: 80-88.
- ↑ Kalmbacher, R., N. Cellinese, et al. (2005). "Seeds obtained by vacuuming the soil surface after fire compared with soil seedbank in a flatwoods plant community." Native Plants Journal 6: 233-241.
- ↑ Ruth, A. D., S. Jose, et al. (2008). "Seed bank dynamics of sand pine scrub and longleaf pine flatwoods of the Gulf Coastal Plain (Florida)." Ecological Restoration 26: 19-21.
- ↑ 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.
- ↑ Maliakal, S.K., E.S. Menges and J.S. Denslow. 2000. Community composition and regeneration of Lake Wales Ridge wiregrass flatwoods in retlation to time-since-fire. Journal of the Torrey Botanical Society 127:125-138.
- ↑ Ruth, A. D., et al. 2008. Seed bank dynamics of sand pine scrub and longleaf pine flatwoods of the Gulf Coastal Plain (Florida). Ecological Restoration 26:19-21.
- ↑ Menges, E. S. and N. M. Kohfeldt (1995). "Life History Strategies of Florida Scrub Plants in Relation to Fire." Bulletin of the Torrey Botanical Club 122(4): 282-297.
- ↑ USDA, NRCS. (2016). The PLANTS Database (http://plants.usda.gov, 25 April 2019). National Plant Data Team, Greensboro, NC 27401-4901 USA.
