|Scientific Name:||Ruppia megacarpa|
|Taxonomic Notes:||The taxonomy of the Ruppia genus is confused. These species can be extremely morphologically variable and respond differently to differing environmental conditions. Therefore, species identifications often link to differences in environmental conditions. This species is potentially a synonym of Ruppia maritima. Flower morphology and genetic studies are needed to evaluate the distribution limits of this species (Larkum et al. 2006).|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Short, F.T., Carruthers, T.J.R., Waycott, M., Kendrick, G.A., Fourqurean, J.W., Callabine, A., Kenworthy, W.J. & Dennison, W.C.|
|Reviewer(s):||Livingstone, S., Harwell, H. & Carpenter, K.E.|
Ruppia megacarpa is found in south western Australia and south eastern Australia. It also has been recorded from South Island in New Zealand. There are no major threats other than localized threats from coastal development and other anthropogenic activities. The overall population is thought to be stable. This species is listed as Least Concern.
|Range Description:||Ruppia megacarpa occurs in south Western Australia, eastern South Australia, and western Victoria, Australia. It also is recorded along the central coast of New South Wales, Australia and in New Zealand.|
Native:Australia; New Zealand
|FAO Marine Fishing Areas:||
Indian Ocean – eastern; Pacific – southwest
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||There is no population information on this species. The overall population is thought to be stable.|
|Current Population Trend:||Stable|
|Habitat and Ecology:||
Ruppia megacarpa is a rhizomatous perennial species that occurs widely in Australia and New Zealand, found growing in permanent water bodies such as estuaries, coastal salt lakes and inland brackish to hypersaline lakes (Jacobs and Brock 1982, Womersley 1984).
Ruppia megacarpa is slow to develop and shows late maturity. The small amount of energy allocated to producing a small number of large propagules appears suitable for interpretation as an example of K-selection (Brock 1983).
|Generation Length (years):||1|
|Major Threat(s):||Localized reduction of this species can be caused by increased sediment loads in water. Coastal development, dredging and marine developments may also locally impact this species.|
|Conservation Actions:||This species is protected in various Marine Protected Areas (MPAs), in Fisheries Acts and National and Marine Park Acts (Green and Short 2003).|
Brock, M.A. 1983. Reproductive allocation in annual and perennial species of the submerged aquatic halophyte Ruppia. The Journal of Ecology 71(3): 811-818.
Green, E.P. and Short, F.T. 2003. World Atlas of Seagrasses. University of California Press, Berkeley.
IUCN. 2010. IUCN Red List of Threatened Species (ver. 2010.3). Available at: http://www.iucnredlist.org. (Accessed: 2 September 2010).
Jacobs, S.W.L. and Brock, M.A. 1982. A revision of the genus Ruppia (Potamogetonaceae) in Australia. Aquatic Botany Amsterdam 14: 325-337.
Larkum, A.W.D., Orth, R.J. and Duarte, C.M. (eds). 2006. Seagrasses: Biology, Ecology and Conservation. Springer, Dordrecht.
Womersley, H.B.S. 1984. The Marine Benthic Flora of Southern Australia. Part I. Handbook of the Flora & Fauna of South Australia. South Australian Government Printing Division, Netley, South Australia.
|Citation:||Short, F.T., Carruthers, T.J.R., Waycott, M., Kendrick, G.A., Fourqurean, J.W., Callabine, A., Kenworthy, W.J. & Dennison, W.C. 2010. Ruppia megacarpa. The IUCN Red List of Threatened Species 2010: e.T173351A6997332. . Downloaded on 25 June 2016.|
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