Ontologia

Coccothrinax jamaicensis

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NTLR Monde (IUCN)
Pays · région · aire protégée · écorégion · biome

Pas d'interactions documentées pour cette espèce.

Liste rouge IUCN

NT · Quasi menacéecritères B2ab(ii,iii,iv)Décroissante
Évaluation complète
Évaluation
2025 · v3.1
Altitude
0305 m
Profondeur
m
État de la populationExpert
No population-level metrics are available. There is a suspected population decline in coastal areas, likely due to habitat quality being affected by increased storm frequency and saltwater intrusion, which pose significant threats to species of the genus Coccothrinax.

Menaces identifiées(4 menaces classées CMP-IUCN)

  • 11_4
    Storms & flooding
    Causing/Could cause fluctuationsUnknownOngoing
  • 1_1
    Housing & urban areas
    Slow, Significant DeclinesUnknownOngoing
  • 11_1
    Habitat shifting & alteration
    Ongoing
  • 2_1_2
    Small-holder farming
    Ongoing
Description complète des menacesExpert
Jestrow et al. (2018) have identified several immediate threats to species of the genus Coccothrinax across the Caribbean, such as oil drilling, nickel mining, saltwater intrusion, urban and agricultural development, low population recruitment, uncontrolled fires, interspecific hybridization, and unsustainable local harvesting for subsistence use.

As well as urban and agricultural development, of the above threats saltwater intrusion caused by tropical storms and climate change leading to coastal erosion and rising sea levels are likely to most impact this coastal palm species. While other Coccothrinax species are known to withstand hurricane-force winds and salt spray without damage, with a mortality rate recorded of 0-2% for four species (Griffith et al. 2013), they are not tolerant of prolonged inundation by salty or brackish water (Florida Native Plant Society 2024).

Recent research shows that the increasing frequency of moderate storms is expected to significantly impact shoreline vegetation through salinization and flooding. Lateral saltwater intrusion, where saltwater moves inland through underground pathways, is a major long-term cause of coastal salinization. However, short-term storm surge events can have an even greater impact through vertical saltwater intrusion, where flooding rapidly pushes saltwater into the ground. The recovery time—how long it takes for groundwater to return to normal salinity after a storm surge—and the depth of saltwater penetration depend on the characteristics of the aquifer, an underground layer of rock or sediment that stores and transports water. After a major hurricane, recovery times for coastal aquifers can range from 10 months to as long as 8 years (Nordio et al. 2023).

Habitats préférentiels (classification IUCN)

  • 1_5Forest - Subtropical/Tropical Dry
  • 2_1Savanna - Dry
  • 3_5Shrubland - Subtropical/Tropical Dry
Mesures de conservation recommandéesExpert
The majority of Jamaican herbarium specimens are located in protected areas according to Protected Planet, including Kingston and St. Andrew Game Reserve, Portland Bight Protected Area, Lovers Leap, The Upper Morass, Black River, St. Elizabeth Game Sanctuary, and Negril Environmental Protection Area. These protected areas often are still exposed to threats of human activities, including illegal farming and agriculture pollution. Specimens in San Andres and Providencia (CO) are located in Area Marina de la Reserva Protegida Mayflower, and those in the Swan Islands (Honduras) are located in Marine Protected Area Abogado Agustin Cordoba Rodriguez (Isla Santanilla o del Cisne) (UNEP-WCMC and IUCN 2024). The Jamaica Forestry Department cultivates and sells Coccothrinax jamaicensis as an ornamental, providing some opportunity for ex situ conservation. Ex situ collections are held in at least four botanic gardens worldwide (BGCI 2024).
Actions de conservation (2)Expert
  • 1_2Resource & habitat protection
  • 2_1Site/area management
Stress écologiques (5)Expert
  • 1_1Ecosystem conversion
  • 1_1Ecosystem conversion
  • 1_2Ecosystem degradation
  • 1_2Ecosystem degradation
  • 2_2Species disturbance
Usage & commerce (3)Expert
  • 12Handicrafts, jewellery, etc.
    subsistance
  • 13Pets/display animals, horticulture
    national
  • 9Construction or structural materials
    subsistance
Priorités de recherche (2)Expert
  • 1_2Population size, distribution & trends
  • 1_4Harvest, use & livelihoods
Niche IUCN globaleExpert

Royaumes biogéographiques

Neotropical

Systèmes (terrestre/eau douce/marin)

Terrestrial

Formes de croissance

Tree - small
Références bibliographiques (13)Expert
  1. IUCN. 2025. The IUCN Red List of Threatened Species. Version 2025-2. Available at: <a href="www.iucnredlist.org">www.iucnredlist.org</a>. (Accessed: 10 October 2025).
  2. Florida Native Plant Society. 2024. <i>Coccothrinax argentata</i>. Available at: <a href="https://www.fnps.org/plant/coccothrinax-argentata">https://www.fnps.org/plant/coccothrinax-argentata</a>.
  3. BGCI. 2024. Botanic Gardens Conservation International (BGCI) - PlantSearch. Available at: <a href="https://tools.bgci.org/plant_search.php">https://tools.bgci.org/plant_search.php</a>. (Accessed: 2024).
  4. UNEP-WCMC and IUCN. 2024. Protected Planet: The World Database on Protected Areas (WDPA) and World Database on Other Effective Area-based Conservation Measures (WD-OECM) [Online]. Cambridge, UK. UNEP-WCMC and IUCN. Available at: <a href="https://www.protectedplanet.net">https://www.protectedplanet.net</a>. (Accessed: 2024).
  5. GBIF. 2024. Global Biodiversity Information Facility. Available at: <a href="https://www.gbif.org/">https://www.gbif.org/</a>.
  6. Nordio G., Frederiks R., Hingst M., Carr J., Kirwan M., Gedan K., Michael H., and Fagherazzi S. 2023. Frequent storm surges affect the groundwater of coastal ecosystems. <i>Geophysical Research Letters</i> 50(1).
  7. Jestrow, B., Peguero, B., Jiménez, F., Verdecia, R., González-Oliva, L., Moya, C.E., Cinea, W., Griffith, M.P., Meerow, A.W., Maunder, M. and Francisco-Ortega, J. 2018. A conservation framework for the Critically Endangered endemic species of the Caribbean palm Coccothrinax. <i>Oryx</i> 52(3): 452-463.
  8. Griffith P.M., Witcher E., Noblick L., Husby C. 2013. Palm Stem Shape Correlates with Hurricane Tolerance, in a Manner Consistent with Natural Selection. <i>Palms</i> 57(3): 115-122.
  9. Bachman, S., Moat, J., Hill, A.W., de la Torre, J. and Scott, B. 2011. Supporting Red List threat assessments with GeoCAT: geospatial conservation assessment tool. In: Smith, B. and Peneb, L. (eds), <i>e-Infrastructure for data publishing in biodiversity science</i>, pp. 117-126. Zoo Keys, 150.
  10. Campbell, K.C.St.E. 2010. <i>Endemic Trees of Jamaica.</i> Institute of Jamaica, Kingston.
  11. Read R.W. 1988. Utilization of indigenous palms in the Caribbean (in relation to their abundance). <i>Advances in Economic Botany</i> 6: 137-143.
  12. Adams, C.D. 1972. <i>Flowering Plants of Jamaica</i>. University of the West Indies, Jamaica.
  13. Read R.W. 1966. <i>Coccothrinax jamaicensis</i>: The Jamaican silver thatch. <i>Principes</i> 10: 133-141.
Évaluateurs & contributeurs (3)Expert
assessor
Vandebroek, I.
evaluator
Balick, M.
facilitators
Barker, A.

Vandebroek, I. 2025. Coccothrinax jamaicensis. The IUCN Red List of Threatened Species 2025: e.T256816097A257325606. Accessed on 05 May 2026.

Répartition mondiale

Aucune observation géoréférencée avec précision suffisante (<10 km) dans GBIF pour cette espèce.

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Observations & statuts

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