
Herbe à tortue
Thalassia testudinumBanks & Sol. ex K.D.Koenig
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Description
espèce de plante aquatique
Source : Wikidata
Pays · région · aire protégée · écorégion · biome
Graphe en cours d’indexation
Calcul du tissu écologique de Thalassia testudinum.
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Liste rouge IUCN
LC · Préoccupation mineure→Stable- Évaluation
- 2010 · v3.1
- Altitude
- – m
- Profondeur
- 10 – 0 m
État de la populationTexte officiel évaluation IUCNExpert
Thalassia testudinum forms extensive dense seagrass beds throughout its range. This is the most important seagrass habitat-forming species in the Caribbean. There have been some declines in seagrass beds in developing areas, particularly in areas of nutrient enrichment and sedimentation. Generally, however, this species still very abundant throughout its range.
Out of 103 published studies on this species, 29 showed an increase in abundance (mix of biomass, aerial extent, or density), 17 decreased and 57 showed no change (Global Seagrass Trajectories Database, Carruthers pers. comm. 2007). The overall population trend is stable.
Caribbean regional biomass ranges from 3.2 g dw/m² (recorded at the latitude 17.8o in the Virgin Islands) to 820 g dw/m² (recorded along the 28.3o latitude on the Florida coast). These findings are summarized in Gacia (1999) and include data from publications ranging from 1959 until 1996.
The T. testudinum population in the Florida Bay covered 90% of mud bank and basins until a massive die off in 1987. Four thousand hectares were completely lost and 24,000 ha were affected due to primary die off caused by higher water temperatures, hypersalinity and increased biomass, leading to high respiration demands. This was followed by secondary die-off from increased turbidity due to increased phytoplankton beginning the fall of 1991. Between 1984 and 1994, mean short shoot density dropped by 22% throughout the Florida Bay and standing crop biomass dropped by 28%. While light attenuation may have been a factor, the patchy distribution of die-off suggests that primary die-off was the principle reason for the decrease in abundance (Hall et al. 1999). Between the spring of 1995 and spring of 1999, despite individual basins in the Florida Bay exhibiting changes in abundance by between 12-100%, the total abundance throughout the Bay exhibited little change due to declines in abundance in the western part of the Bay being offset by increases in abundance in the central and eastern basins (Durako and Hall 2000). Increases in seagrass coverage along with large occurrences of flowering plants were observed during the spring of 2000; however, primary die-off among high density stands was also observed north of Barneys Key with similar symptoms noted to the 1987 die-off (Nuttle et al. 2003).
Out of 103 published studies on this species, 29 showed an increase in abundance (mix of biomass, aerial extent, or density), 17 decreased and 57 showed no change (Global Seagrass Trajectories Database, Carruthers pers. comm. 2007). The overall population trend is stable.
Caribbean regional biomass ranges from 3.2 g dw/m² (recorded at the latitude 17.8o in the Virgin Islands) to 820 g dw/m² (recorded along the 28.3o latitude on the Florida coast). These findings are summarized in Gacia (1999) and include data from publications ranging from 1959 until 1996.
The T. testudinum population in the Florida Bay covered 90% of mud bank and basins until a massive die off in 1987. Four thousand hectares were completely lost and 24,000 ha were affected due to primary die off caused by higher water temperatures, hypersalinity and increased biomass, leading to high respiration demands. This was followed by secondary die-off from increased turbidity due to increased phytoplankton beginning the fall of 1991. Between 1984 and 1994, mean short shoot density dropped by 22% throughout the Florida Bay and standing crop biomass dropped by 28%. While light attenuation may have been a factor, the patchy distribution of die-off suggests that primary die-off was the principle reason for the decrease in abundance (Hall et al. 1999). Between the spring of 1995 and spring of 1999, despite individual basins in the Florida Bay exhibiting changes in abundance by between 12-100%, the total abundance throughout the Bay exhibited little change due to declines in abundance in the western part of the Bay being offset by increases in abundance in the central and eastern basins (Durako and Hall 2000). Increases in seagrass coverage along with large occurrences of flowering plants were observed during the spring of 2000; however, primary die-off among high density stands was also observed north of Barneys Key with similar symptoms noted to the 1987 die-off (Nuttle et al. 2003).
Menaces identifiées(12 menaces classées CMP-IUCN)
1_1Housing & urban areasOngoing1_2Commercial & industrial areasOngoing1_3Tourism & recreation areasOngoing4_3Shipping lanesOngoing5_4_4Unintentional effects: (large scale) [harvest]Ongoing5_4_6Motivation Unknown/UnrecordedOngoing6_1Recreational activitiesOngoing9_1_1SewageOngoing9_1_3Type Unknown/UnrecordedOngoing9_2_3Type Unknown/UnrecordedOngoing
+ 2 menaces supplémentaires
Description complète des menacesTexte détaillé évaluation IUCNExpert
The biggest threats to Thalassia testudinum are coastal development, eutrophication, and sedimentation (T. Carruthers, F. Short, B. van Tussenbroek, J. Zieman pers. comm. 2007). Boat traffic, marina development, and sewage pollution from greatly expanded residential and hotel development is a particular problem in Florida. Trawling is also a threat in some parts of the range.
Habitats préférentiels (classification IUCN)
9_10Marine Neritic - Estuaries9_3Marine Neritic - Subtidal Loose Rock/pebble/gravel9_4Marine Neritic - Subtidal Sandy9_5Marine Neritic - Subtidal Sandy-Mud9_6Marine Neritic - Subtidal Muddy9_8_2Back Slope9_8_4Lagoon9_8_5Inter-Reef Soft Substrate9_8_6Inter-Reef Rubble Substrate9_9Marine Neritic - Seagrass (Submerged)12_2Marine Intertidal - Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc
Mesures de conservation recommandéesStratégies de conservation IUCNExpert
The range of Thalassia testudinum falls in some Marine Protected Areas (MPAs). In the Caribbean, T. testudinum is included in the 24 fully managed marine protected areas. This species is monitored by the CARICOMP network (Caribbean Coastal Marine Productivity network), including coral reefs and mangroves (Green and Short 2003). Currently, a seagrass management plan is being developed in Bermuda (Sarkis pers. comm. 2007). This species is also listed as Vulnerable (A2a) under the Bermuda Protected Species Act (Sarkis pers. comm. 2007).
This is a major habitat-forming species in the Greater Caribbean and should be monitored (Van Tussenbroek et al. 2006).
This is a major habitat-forming species in the Greater Caribbean and should be monitored (Van Tussenbroek et al. 2006).
Stress écologiques (17)Stresses Classification — IUCNExpert
1_1Ecosystem conversion1_1Ecosystem conversion1_1Ecosystem conversion1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation1_2Ecosystem degradation2_2Species disturbance2_2Species disturbance2_2Species disturbance
Priorités de recherche (1)Research Needed Classification — IUCNExpert
3_1Population trends
Niche IUCN globaleRealms · Systems · LMEs · Growth forms · FAOs — biogéographie IUCNExpert
Systèmes (terrestre/eau douce/marin)
Marine
Formes de croissance
Graminoid
Zones de pêche FAO
Atlantic - western centralPacific - eastern central
Références bibliographiques (22)Sources scientifiques de l'évaluation IUCNExpert
- IUCN. 2010. IUCN Red List of Threatened Species (ver. 2010.3). Available at: <a href="http://www.iucnredlist.org">http://www.iucnredlist.org</a>. (Accessed: 2 September 2010).
- Larkum, A.W.D., Orth, R.J. and Duarte, C.M. (eds). 2006. <i>Seagrasses: Biology, Ecology and Conservation</i>. Springer, Dordrecht.
- van Tussenbroek, B.I., Vonk, J.A., Stapel, J., Erftemeijer, P.A., Middelburg, J.L. and Zieman, J.C. 2006. The biology of Thalassia: paradigms and recent advances in research. In: A.W.D. Larkum, R.J. Orth and C.M. Duarte (eds), <i>Seagrasses: Biology, Ecology and Conservation</i>, pp. 409-439. Springer, Dordrecht.
- Hale, J.A., Frazer, T.K., Tomasko, D.A. and Hall, M.O. 2004. Changes in the distribution of seagrass species along Florida's central Gulf Coast: Iverson and Bittaker revisited. <i>Estuaries</i> 27(1): 36-43.
- Dawes, C.J., Phillips, R.C. and Morrison, G. 2004. <i>Seagrass Communities of the Gulf Coast of Florida: Status and Ecology</i>. St. Petersburg, Florida.
- Fourqurean, J.W. and Rutten, L.M. 2004. The impact of Hurrican Georges on soft-bottom, back reef communities: site- and species-specific effects in south Florida seagrass beds. <i>Bulletin of Marine Science</i> 75(2): 237-257.
- Green, E.P. and Short, F.T. 2003. <i>World Atlas of Seagrasses</i>. University of California Press, Berkeley.
- Nuttle, W., Hunt, J. and Robblee, M. 2003. Florida Bay Science Program: A Synthesis of Research on Florida Bay.
- Hemminga, M.A. and Duarte, C.M. 2000. <i>Seagrass Ecology</i>. Cambridge University Press, Cambridge.
- Durako, M.J. and Hall, M.O. 2000. After the die-off: Seagrass dynamics in a perturbed subtropical lagoon. <i>Biologia Marina Mediterranea</i> 7(2): 365-368.
- Duarte, C.M. and Chiscano, C.L. 1999. Seagrass biomass and production: A reassessment. <i>Aquatic Botany</i> 65: 159-174.
- Gacia, E. 1999. Leaf dynamics and shoot production of the seagrass <i>Thalassia testudinum</i> in the Indian River Lagoon. <i>Botanica Marina</i> 42: 97-102.
- Hall, M.O., Durako, M.J., Fourqurean, J.W. and Zieman, J.C. 1999. Decadal changes in seagrass distribution and abundance in Florida Bay. <i>Estuaries</i> 22(2B): 445-459.
- UNESCO. 1998. CARICOMP-Caribbean coral reef, seagrass and mangrove sites. Coastal region and small island papers. UNESCO, Paris.
- Fourqurean, J.W., Powell, G.V.N., Kenworthy, W.J. and Zieman, J.C. 1995. The effects of long term manipulation of nutrient supply on competition between the seagrasses <i>Thalassia testudinum</i> and <i>Haludule wrightii</i> in Florida Bay. <i>OIKOS</i> 72: 349-358.
- Iverson, R.L. and Bittaker, H.F. 1986. Seagrass distribution and abundance in eastern Gulf of Mexico coastal waters. <i>Estuarine, Coastal and Shelf Science</i> 22: 577-602.
- Zieman, J.C. 1982. The ecology of the seagrasses of South Florida: a community profile. <i>US Fish and Wildlife Service Biological Services Program</i> FWS/OBS-82/5: 150.
- Phillips, R.C., McMillan, C. and Bridges, K.W. 1981. Phenology and reproductive physiology of <i>Thalassia testudinum</i> from the western tropical Atlantic. <i>Aquatic Botany</i> 11: 263-277.
- Lewis, R.R. and Phillips, R.C. 1980. Occurrence of seeds and seedlings of <i>Thalassia testudinum</i> Banks ex Konig in the Florida Keys (USA). <i>Aquatic Botany</i> 9: 377-380.
- Buesa, R.J. 1975. Population biomass and metabolic rates of marine angiosperms on the Northwestern Cuban Shelf. <i>Aquatic Botany</i> 1: 11-23.
- Fuss, C.M. and Kelly, J.A., Jr. 1969. Survival and growth of seagrasses transplanted under artificial conditions. <i>Bulletin of Marine Science</i> 19: 351-365.
- Phillips, R.C. 1960. Observations on the ecology and distribution of the Florida seagrasses. <i>Florida Board of Conservation Professional Paper Series</i> 2: 1-72.
Évaluateurs & contributeurs (2)Personnes ayant contribué à l'évaluation IUCNExpert
assessor
Short, F.T., Carruthers, T.J.R., van Tussenbroek, B. & Zieman, J.
evaluator
Livingstone, S., Harwell, H. & Carpenter, K.E.
Short, F.T., Carruthers, T.J.R., van Tussenbroek, B. & Zieman, J. 2010. Thalassia testudinum. The IUCN Red List of Threatened Species 2010: e.T173346A6995927. Accessed on 05 May 2026.
Distribution mondiale
Calcul de la distribution GBIF· ~10–60 s
Phénologie
Calcul du calendrier d'apparition· ~5–30 s
Consulter sur les bases externes
Observations & statuts
Cartographie
Note nomenclaturale & synonymesDétails taxonomiques + synonymes CoLExpert
Note nomenclaturale
TAXREF v18 — INPN/MNHNSynonymes (1)— redirigent vers cette page
- Thalassia vitrariorumPers.
Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).