Ontologia
Herbe à tortue

Herbe à tortue

Thalassia testudinumBanks & Sol. ex K.D.Koenig

LCLR Monde (IUCN)
1 photo · Licences CC (Wikimedia Commons / iNaturalist)Click pour agrandir

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.

Le graphe apparaîtra automatiquement dès que le calcul est terminé (rafraîchissement toutes les 5s).

Liste rouge IUCN

LC · Préoccupation mineureStable
Évaluation complète
Évaluation
2010 · v3.1
Altitude
m
Profondeur
100 m
État de la populationExpert
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).

Menaces identifiées(12 menaces classées CMP-IUCN)

  • 1_1
    Housing & urban areas
    Ongoing
  • 1_2
    Commercial & industrial areas
    Ongoing
  • 1_3
    Tourism & recreation areas
    Ongoing
  • 4_3
    Shipping lanes
    Ongoing
  • 5_4_4
    Unintentional effects: (large scale) [harvest]
    Ongoing
  • 5_4_6
    Motivation Unknown/Unrecorded
    Ongoing
  • 6_1
    Recreational activities
    Ongoing
  • 9_1_1
    Sewage
    Ongoing
  • 9_1_3
    Type Unknown/Unrecorded
    Ongoing
  • 9_2_3
    Type Unknown/Unrecorded
    Ongoing

+ 2 menaces supplémentaires

Description complète des menacesExpert
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 - Estuaries
  • 9_3Marine Neritic - Subtidal Loose Rock/pebble/gravel
  • 9_4Marine Neritic - Subtidal Sandy
  • 9_5Marine Neritic - Subtidal Sandy-Mud
  • 9_6Marine Neritic - Subtidal Muddy
  • 9_8_2Back Slope
  • 9_8_4Lagoon
  • 9_8_5Inter-Reef Soft Substrate
  • 9_8_6Inter-Reef Rubble Substrate
  • 9_9Marine Neritic - Seagrass (Submerged)
  • 12_2Marine Intertidal - Sandy Shoreline and/or Beaches, Sand Bars, Spits, Etc
Mesures de conservation recommandéesExpert
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).
Stress écologiques (17)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_2Species disturbance
  • 2_2Species disturbance
  • 2_2Species disturbance
Priorités de recherche (1)Expert
  • 3_1Population trends
Niche IUCN globaleExpert

Systèmes (terrestre/eau douce/marin)

Marine

Formes de croissance

Graminoid

Zones de pêche FAO

Atlantic - western centralPacific - eastern central
Références bibliographiques (22)Expert
  1. 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).
  2. Larkum, A.W.D., Orth, R.J. and Duarte, C.M. (eds). 2006. <i>Seagrasses: Biology, Ecology and Conservation</i>. Springer, Dordrecht.
  3. 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.
  4. 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.
  5. 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.
  6. 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.
  7. Green, E.P. and Short, F.T. 2003. <i>World Atlas of Seagrasses</i>. University of California Press, Berkeley.
  8. Nuttle, W., Hunt, J. and Robblee, M. 2003. Florida Bay Science Program: A Synthesis of Research on Florida Bay.
  9. Hemminga, M.A. and Duarte, C.M. 2000. <i>Seagrass Ecology</i>. Cambridge University Press, Cambridge.
  10. 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.
  11. Duarte, C.M. and Chiscano, C.L. 1999. Seagrass biomass and production: A reassessment. <i>Aquatic Botany</i> 65: 159-174.
  12. 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.
  13. 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.
  14. UNESCO. 1998. CARICOMP-Caribbean coral reef, seagrass and mangrove sites. Coastal region and small island papers. UNESCO, Paris.
  15. 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.
  16. 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.
  17. 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.
  18. 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.
  19. 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.
  20. Buesa, R.J. 1975. Population biomass and metabolic rates of marine angiosperms on the Northwestern Cuban Shelf. <i>Aquatic Botany</i> 1: 11-23.
  21. 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.
  22. 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)Expert
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.

Répartition mondiale (heatmap GBIF)Construction en cours

0 obs · 0 cellules
Construction par partitions temporelles GBIF0%

Source : GBIF — observations agrégées par hexagones 0.2° × 0.2° (~22km). Filtre qualité : précision coordonnée < 10 km. Coloration quantile (q50/70/90/99). Fond carte : OpenFreeMap · © OpenStreetMap.

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

Bibliographie

Note nomenclaturale & synonymesExpert

Note nomenclaturale

TAXREF v18 — INPN/MNHN

Synonymes (1)— redirigent vers cette page

  • Thalassia vitrariorumPers.

Sources : Catalogue of Life Cross-References (synonymes) · TAXREF v18 INPN/MNHN (commentaires FR).